Bacterial strains that degrade polyaromatic hydrocarbons

ABSTRACT

Polyaromatic hydrocarbons are found in contaminated soils and groundwater and are a large class of compounds for which treatment by bioremediation is sought. Accordingly, indigenous organisms that can degrade polyaromatic hydrocarbon are needed. Presented are strains of the Paenibacillus genus that degrade low molecule weight polyaromatic, and, in the presence of phenanthrene, high molecular weight polyaromatic hydrocarbons. These bacteria strains are unique among PAH-degrading bacterial strains because they form endospores and therefore can survive adverse environmental conditions. Among the strains presented are several from “ P. naphthalenovorans ”, a newly described species. Also presented are compositions for bioremediation comprising the bacterial strains of the invention, and a method for isolating the strains and a method for using the strains for bioremediation.

[0001] This application claims priority to U.S. Provisional Application No. 60/096,769, filed Aug. 17, 1998, which is incorporated in its entirety by reference herein.

FIELD OF THE INVENTION

[0002] This invention relates to the field of bacterial strains used for bioremediation. In particular, it relates to endospore-forming bacterial strains that can degrade polyaromatic hydrocarbons, and methods to isolated these bacterial strains and to use these strains for bioremediation.

BACKGROUND OF THE INVENTION

[0003] Various scientific and scholarly articles are referred to throughout the specification. These articles are incorporated by reference herein to describe the state of the art to which this invention pertains.

[0004] Polyaromatic hydrocarbons (PAHs) are widespread pollutants, particularly in conjunction with the marine environment. High PAH levels are known to be toxic, mutagenic and carcinogenic, and therefore pose a considerable threat to the public health. Many microorganisms degrade PAHs, and there is a strong interest in applying bioremediation approaches to remove PAHs from the environment.

[0005] Bacteria that degrade 2-3 ring low molecular weight polyaromatic hydrocarbons, such as naphthalene, phenanthrene, bi-phenyl and fluorene, are taxonimically diverse. Gram negative genera such as Pseudomonas, Burkholderia, Alcaligens, Sphingomonas, Vibrio and Comamonas are common. While less common, the gram-positive species such as Mycobacterium, Nocardla, Rhodococcus and Gordona are also known to degrade low molecular weight PAHs.

[0006] Microorganisms that can degrade the 4-ring and higher high molecular weight PAHs such as pyrene, fluoranthene and benz[a]anthracene are much rarer. The degradation of high molecular weight PAHs is much slower and less extensive than the degradation of low molecular weight PAHs in the environment.

[0007] The isolation of new genera of PAH-degrading bacteria is sought, particularly species with novel combinations of growth and degradative characteristics. In particular, species are sought with a broad range of PAH specificities. Species that can degrade the higher molecular weight PAHs are particularly valuable. Finally, PAH-degrading species that are capable to surviving adverse nutritional and environmental conditions by forming endospores are of particular interest.

SUMMARY OF THE INVENTION

[0008] The invention pertains to isolated strains of bacteria that degrade polyaromatic hydrocarbons, a method of isolating the strains of the invention and a method of using the strains of the invention for bioremediation. The bacterial strains are in the family Bacillaceae and are novel for their combination of PAH-degrading and endospore-forming properties. These bacterial strains have utility for bioremediation of polyaromatic hydrocarbon in contaminated environments.

[0009] The first aspect of the invention is an isolated strain in the family Bacillaceae that has broad PAH-degrading capabilities in that it degrades at least two of the PAHs naphthalene, phenanthrene and biphenyl. In a preferred embodiment, the strain additionally degrades pyrene when induced by phenanthrene. Preferably, the strain is in the isolate Paenibacillus, and most preferably in the species P. validus. This isolated bacterial strain may be isolates PR-P1, PR-N4 and PR-B2, which are ATCC Accession Nos. [not yet assigned], [not yet assigned] and [not yet assigned], respectively.

[0010] The second aspect of the invention is an isolated bacterial strain that is the newly described species “Paenibacillus naphthalenovorans” and degrades naphthalene. This bacterial strain is further described by several features. The strain has, in a preferred embodiment, a whole cell fatty acid composition in which 16:1 ω11c fatty acids comprise at least 8.8%, and additionally, in a most preferred embodiment, at least 5.8% but not more than 10.0% 17:0 anteiso fatty acids, when grown on trypticase soy agar at 28° C. for 24 hours prior to analysis. In another preferred embodiment, the isolated strain has a whole cell fatty acid similarity index as compared to isolate PR-N1 of greater than 0.4 when grown on trypticase soy agar at 28° C. for 24 hours prior to analysis. In another preferred embodiment, the bacterial strain has a 16S rRNA gene sequence that is at least about 95% homologous to SEQ ID NO:8. In another preferred embodiment, the genomic DNA of the strain exhibits at least 10% binding to the genomic DNA of isolate PR-N1. In another preferred embodiment, the strain is ATCC Accession No. [not yet assigned].

[0011] Another aspect of the invention is a plurality of bacterial strains that degrade PAHs. This plurality comprises at least two of the following: Paenibacillus validus, a sphingomonad, an Arthrobacter, “Paenibacillus naphthalenovorans” and a nocardioform. In a preferred embodiment, the P. validus strain is ATCC Accession No. [not yet assigned] and the “P. naphthalenovorans” strain is ATCC Accession No. [not yet assigned].

[0012] Another aspect of the invention is a composition for bioremediation that comprises one of the aforementioned bacterial strains and an ecologically acceptable carrier.

[0013] Another aspect of the invention is a method for removing PAHs from a substrate comprising contacting the substrate with the bacterial strain of the invention for a time sufficient to remove the PAHs. In preferred embodiments, the substrate of the method is solid or liquid, with optional aeration. In a more preferred embodiment, the method additionally comprises planting plants in the substrate, and in a most preferred embodiment, the plant is Spartina alterniflora. In another most preferred embodiment, the method has the additional step of inducing of the bacterial strain with phenanthrene.

[0014] Another aspect of the invention is a method to isolate endospore-forming PAH-degrading bacterial strains. This method comprises the steps of growing a heterogenous culture with a PAH as the sole carbon source, and heating the culture to a temperature for a time sufficient to kill vegetative bacteria. In preferred embodiments, the PAHs used are naphthalene, phenanthrene or biphenyl. In another preferred embodiment, the culture is heated to 70 to 90° C. for 10 to 20 minutes.

[0015] Other features and advantages of the present invention will be better understood by reference to the drawings, detailed description and examples that follow.

BRIEF DESCRIPTION OF THE DRAWINGS

[0016]FIG. 1. Euclidean distance dendrogram based on the whole-cell fatty acid compositions of all the PAH-degrading strains isolated by enrichment from sediment and rhizosphere samples obtained from Lewes, Del. and Piles Creek, N.J. The aerobic (TSBA) library version 3.9 of the Microbial Identification System (MIDI Inc, Newark, DE) was used to perform a comparative analysis.

[0017]FIG. 2. Euclidean distance dendrogram based on the whole-cell fatty acid compositions of the sediment and rhizosphere PAH-degrading Paenibacillus isolates. Piles Creek sediment and Spartina alterniflora rhizosphere isolates are denoted as PS and PR, respectively. Isolates obtained from the rhizosphere of Sporobolus aeroides, Distichlis spicata or Juncus gerardi are denoted as SA, DS or JG, respectively. In addition, strains isolated using naphthalene are indicated by an N, while phenanthrene and biphenyl enriched isolates are denoted by a P and B, respectively. American Type Culture Collection (ATCC) reference strains are in black. The dendrogram program for the Microbial Identification System (MIDI, Inc.) was used to perform a comparative analysis.

[0018]FIG. 3. Two-dimensional plot of the gram-positive endospore-forming PAH-degrading isolates generated by principle-component analysis of whole-cell fatty acid profiles showing distribution into two main groups: Group 1 corresponds to the nonmucoid Paenibacillus validus group and Group 2 represents the novel Paenibacillus species group exhibiting a mucoid colony morphology.

[0019]FIG. 4. Neighbor-joining phylogenetic tree of the PAH-degrading isolates and the major groups of the genera Bacillus, Brevibacillus and Paenibacillus. The tree was constructed using a 368 bp alignment of the 16S rRNA gene. All sequences were aligned to sequences extracted from the Ribosomal Database Project (Michigan State University, East Lansing Mich., Center for Microbial Ecology) using GDE software (Maidak et al., 1999 Nucleic Acids Res. 27:171-173).

[0020]FIG. 5A. Degradation of fluoranthene by Paenibacillus strain PR-P1 over a seven day time course. The three treatments compared include the addition of 10 ppm phenanthrene, strain PR-P1 only and an uninoculated control. Results are the mean of triplicate cultures±standard deviation. Square data points are PR-P1+10 ppm phenanthrene; circular data points are PR-P1 only; and triangular data points are the uninoculated control. FIG. 5B. Degradation of pyrene by Paenibacillus strain PR-P1 over a seven day time course. The three treatments compared include the addition of 10 ppm phenanthrene, strain PR-P1 only and an uninoculated control. Results are the mean of triplicate cultures±standard deviation. Square data points are PR-P1+10 ppm phenanthrene; circular data points are PR-P1 only; and triangular data points are the uninoculated control.

[0021]FIG. 6A. Degradation of fluoranthene after seven days incubation in the presence of the bacterial consortium and 10 ppm phenanthrene. Results are the mean of triplicate cultures±standard deviation. From left to right, the bars refer to the treatments consortium+phenanthrene; consortium+phenanthrene+salicylate; consortium+phenanthrene+Tween-80; phenanthrene+Tween-80; and killed consortium+Tween-80. FIG. 6B. Degradation of pyrene after seven days incubation in the presence of the bacterial consortium and 10 ppm phenanthrene. Results are the mean of triplicate cultures ±standard deviation. From left to right, the bars refer to the treatments consortium+phenanthrene; consortium+phenanthrene+salicylate; consortium+phenanthrene+Tween-80; phenanthrene+Tween-80; and killed consortium+.Tween-80. FIG. 6C. Degradation of benz[a]anthracene after seven days incubation in the presence of the bacterial consortium and 10 ppm phenanthrene. Results are the mean of triplicate cultures±standard deviation. From left to right, the bars refer to the treatments consortium+phenanthrene; consortium+phenanthrene+salicylate; consortium+phenanthrene+Tween-80; phenanthrene+Tween-80; and killed consortium+Tween-80.

DETAILED DESCRIPTION OF THE INVENTION

[0022] I. Definitions

[0023] Various terms relating to the biological molecules used to describe the present invention are used hereinabove and also throughout the specification and claims.

[0024] With reference to nucleic acids, the term “isolated nucleic acid” is sometimes used. This term, when applied to DNA, refers to a DNA molecule that is separated from sequences with which it is immediately contiguous (in the 5′ and 3′ directions) in the naturally occurring genome of the organism from which it was derived. For example, the “isolated nucleic acid” may comprise a DNA molecule inserted into a vector, such as a plasmid or virus vector, or integrated into the genomic DNA of a prokaryote or eukaryote. An “isolated nucleic acid molecule” may also comprise a cDNA molecule.

[0025] With respect to RNA molecules, the term “isolated nucleic acid” primarily refers to an RNA molecule encoded by an isolated DNA molecule as defined above. Alternatively, the term may refer to an RNA molecule that has been sufficiently separated from RNA molecules with which it would be associated in its natural state (i.e., in cells or tissues), such that it exists in a “substantially pure” form (the term “substantially pure” is defined below).

[0026] The term “substantially pure” refers to a preparation comprising at least 50-60% by weight the compound of interest (e.g., nucleic acid, oligonucleotide, protein, etc.). More preferably, the preparation comprises at least 75% by weight, and most preferably 90-99% by weight, the compound of interest. Purity is measured by methods appropriate for the compound of interest (e.g. chromatographic methods, agarose or polyacrylamide gel electrophoresis, HPLC analysis, and the like).

[0027] With respect to single stranded nucleic acid molecules, the term “specifically hybridizing” refers to the association between two single-stranded nucleic acid molecules of sufficiently complementary sequence to permit such hybridization under predetermined conditions generally used in the art (sometimes termed “substantially complementary”). In particular, the term refers to hybridization of an oligonucleotide with a substantially complementary sequence contained within a single-stranded DNA or RNA molecule of the invention, to the substantial exclusion of hybridization of the oligonucleotide with single-stranded nucleic acids of non-complementary sequence.

[0028] The term “substantially the same” refers to nucleic acid or amino acid sequences having sequence variation that do not materially affect the nature of the protein (i.e. the structure, stability characteristics and/or biological activity of the protein). With particular reference to nucleic acid sequences, the term “substantially the same” is intended to refer to the coding region and to conserved sequences governing expression, and refers primarily to degenerate codons encoding the same amino acid, or alternate codons encoding conservative substitute amino acids in the encoded polypeptide. With reference to amino acid sequences, the term “substantially the same” refers generally to conservative substitutions and/or variations in regions of the polypeptide not involved in determination of structure or function.

[0029] The terms “percent identical” and “percent homologous” are also used herein in comparisons among nucleic acid sequences. “Percent identical” and “percent homologous” refers to the percent of the nucleotides of the subject nucleic-acid sequence that have been matched to identical nucleotides by a sequence analysis program. With respect to the present invention, the percent identity of nucleic acid sequences is determined by the PILEUP program in the Genetics Computer Group (GCG) software package using the default parameters

[0030] II. Description

[0031] Provided with the present invention are two species of bacteria that have useful properties for bioremediation, and methods to isolate and use these species for bioremediation. The two bacteria species have been found to be able to degrade polycyclic aromatic hydrocarbons. This ability makes these two species very useful for the bioremediation of soils and waters contaminated with polycyclic aromatic hydrocarbons (PAHs). These bacterial species also possess the useful ability to form endospores in order to survive adverse conditions. The first species, Paenibacillus validus, has the ability to degrade a broad spectrum of low molecular weight PAHs, including naphthalene, phenanthrene, bi-phenyl, p-hydroxybenzoate and benzoate, as well as the higher molecular weight PAHs such as pyrene and fluoranthene when induced by phenanthrene. This species was not previously known to degrade such a broad range of PAHs.

[0032] The second species, tentatively named “Paenibacillus naphthalenovorans”, is a PAH-degrading species heretofore unidentified. Provided herein are characteristics such as whole cell fatty acid composition, rRNA gene sequence and phenotypic characteristics that define “Paenibacillus naphthalenovorans” as a novel species. In conjunction with its initial description herein is the discovery that this new species degrades naphthalene and m-hydroxybenzoate and is useful for bioremediation.

[0033] Also provided is a method to use these two bacterial species to treat contaminated sediment, soil or water, as well as a method to isolate endospore-forming bacterial strains that degrade PAHs.

[0034] In accordance with the present invention, rhizosphere soil samples and sediment samples were collected from salt marshes and an estuary in Delaware and New Jersey. These site were categorized as pristine or contaminated with PAHs. The bacterial populations from these samples were enriched for PAH-degrading species by growth on naphthalene, phenanthrene or biphenyl as the sole carbon source (Example 1). Isolated strains were morphologically and phenotypically characterized and compared to type strains using phase-contrast microscopy, whole cell fatty acid profiles and assorted biochemical tests standard in bacterial identification. Heat treatment was used to screen for endospore-forming gram-positive bacteria that would have useful survival properties. The use of heat treatment in conjunction with the isolation of PAH-degrading bacteria is novel and specifically isolates endospore-forming bacteria the degrade PAHs.

[0035] The resulting isolates were categorized as gram-negative or gram-positive. Tentative identification based on whole cell fatty acid composition led to assignments of genus to the isolates (Tables 2-4). Several gram-negative bacterial species were isolated, mostly from the genus Pseudomonas but also from Alcaligenes and Flavobacterium. The gram-positive isolates mainly fell into the genera of Paenibacillus, Nocardia, Mycobacterium and Arthrobacter. None of the strains tested was particularly effective at metabolizing pyrene, while all could metabolize naphthalene with high efficiency, and biphenyl, fluorene and phenanthrene with varying degrees of efficiency.

[0036] The “Bacillus” isolates were all from the genus Paenibacillus. The discovery of Paenibacillus isolates that could degrade PAHs, and particularly phenanthrene, is novel. These species of bacteria are very desirable for bioremediation efforts because of their ability to form endospores during times of nutrient limitation or adverse environmental conditions. These endospores can remain dormant for many years and retain the ability to germinate and form vegetative cells. The ability to form endospores gives these bacteria a longevity and stability in the environment not found in other bacteria.

[0037] The Paenibacillus isolates were characterized further with whole cell fatty acid analyses, phenotypic characteristics, G+C content, rRNA gene sequence and DNA binding experiments (Ash et al., 1993, Antonie Van Leeuwenhoek, 64:253-260; incorporated by reference herein). 16S rRNA gene phylogenetic analysis and fatty acid analysis determined that the isolates were members of the genus Paenibacillus with a high percent of 15:0 anteiso, 15:0 iso, 16:0 iso, 17:0 iso and 17:0 anteiso fatty acids typical of the genus Paenibacillus (Table 6).

[0038] Colony morphology divided the isolates into two groups, mucoid and nonmucoid. When used in accordance with the bacterial species of the present invention, mucoid morphology is defined as producing slimy colonies on tryptic soy agar. The amount of 10:0 iso, 16:1 ω11c and 16:0 fatty acids also distinguished between these two groups (Table 6), as does partial rRNA gene sequence analysis. While both groups have rRNA gene sequences with significant homology to the P. validus rRNA gene, the nonmucoid group has higher homologies, 95-98%, than the mucoid group, 93-95%. Fatty acid analysis and rRNA gene sequences determined that the nonmucoid Paenibacillus isolates were from the known species P. validus, while the mucoid colony isolates were from a novel species. This novel species has been tentatively named “Paenibacillus naphthalenovorans”.

[0039] Further differences were found in phenotypic characteristics of the isolates of the two groups in the Voges-Proskauer test and esculin hydrolysis; and the ability to produce acid from glycerol, ribose, D-xylose, dulcitol, inositol, amidon and glycogen (Table 8). The two groups also differed in their ability to grow-on aromatic substrates (Table 9). The nonmucoid P. validus isolates metabolized a wider range of aromatic substrates including naphthalene, phenanthrene, biphenyl, p-hydroxybenzoate and benzoate, but not m-hydroxybenzoate. The mucoid “P. naphthalenovorans” isolates can grow on naphthalene, p-hydroxybenzoate, benzoate and m-hydroxybenzoate, but not phenanthrene and biphenyl. When induced by phenanthrene, P. validus strain PR-P1 was found to degrade the high molecule weight PAHs pyrene and fluoranthrene.

[0040]Paenibacillus validus (Pichinoty et al., 1986, Ann. Inst. Pastuer/Microbiol. 137A:65-78; Nakamura et al., 1984, Int. J. Sys. Bacteriol. 34:410-413; both are incorporated by reference herein) is an established species, and as such there are established characteristics that may be used to identify strains of this species. This species is now defined to encompass the species Paenibacillus gordonae (formerly Bacillus gordonae) (Heyndrickx et al., 1995, Int. J. Sys. Bacteriol. 45:661-669; incorporated by reference herein). Defining species characteristics include similarity to the P. validus type strain (ATCC Accession No. 43897). Such defining characteristics are well known in the art and include similarity of 16S rRNA gene sequence, whole cell fatty acid profile and phenotypic characteristics.

[0041] In accordance with the invention, isolates of P. validus have been discovered that will grow with the low molecular weight PAHs phenanthrene and biphenyl as the sole carbon source. Of the PAHs naphthalene, phenanthrene and biphenyl, the isolated bacterial strain of the invention will grow on at least two in a preferred embodiment, and all three in a most preferred embodiment.

[0042] Also in accordance with the present invention it is now known that P. validus isolates will degrade the high molecular weight PAHs fluoranthene and pyrene when induced by phenanthrene. The ability of bacteria to degrade these high molecular weight is very rare and these compounds therefore persist in the sediment. It is contemplated that the metabolic stimulation by phenanthrene will also occur in many Bacillaceae species.

[0043] Example 3 contains the description of several PAH-degrading isolates of P. validus. Isolates PR-P1, PR-N4 and PR-B2 have been deposited with the American Type Culture Collection as accession numbers [not yet assigned, not yet assigned, not yet assigned], respectively. Taught herein are the whole cell fatty acid profiles of 14 isolates (Table 6), the phenotypic characteristics of 6 isolates (Table 8), the 16S rRNA gene sequences of 5 isolates (SEQ ID NOs:1-5), the mole percent G+C of 4 isolates (Table 10), and percent genomic DNA binding for 2 isolates (Table 10) and the PAH-degrading properties of 3 isolates (Table 9). It is contemplated that by teaching the characteristics of this group of isolates, that the isolated bacterial strain of the invention includes all PAH-degrading strains isolated in the species P. validus.

[0044]Paenibacillus validus is the first known species in the Bacillaceae that is able to degrade a wide variety of PAHs. The Bacillaceae contain species of gram positive, motile, rod-shaped bacteria that form endospores. Given the highly related nature of bacteria in this group, it is very likely other genera of the group will also contain members with PAH-degrading capabilities. It is therefore contemplated that the isolation of several PAH-degrading strains in the family Bacillaceae will lead to the isolation of many more from all the genera. The isolated bacterial strain of the invention is therefore contemplated to encompass all species that metabolize PAHs in addition to naphthalene in the family Bacillaceae. In a preferred embodiment, the isolated bacterial strain is in the genus Paenibacillus (Ash et al., 1993, Antonie van Leeuwenhoek 64:253-260; Shida et al., 1997, Int. J. Sys. Bacteriol. 47:289-298; all are incorporated by reference herein). In the most preferred embodiments, the bacterial strain is P. validus.

[0045] The second isolated bacterial strain of the invention is in the newly discovered species, “Paenibacillus naphthalenovorans”. Isolate PR-N1 has been deposited in the American Type Culture Collection as representative of this new species (ATCC Accession No. [not yet assigned]).

[0046] In accordance with the present invention, the first isolation of “P. naphthalenovorans” strains are taught in Example 1, and a use for these strains in bioremediation is taught in Example 3. It is therefore contemplated that another aspect of the instant invention is an isolated bacterial strain that is an isolated strain of “P. naphthalenovorans”.

[0047] In accordance with the present invention, “Paenibacillus naphthalenovorans” is defined by the characteristics traditionally used in the art to define bacterial species: 16S rRNA gene sequence, percent genomic DNA binding, whole cell fatty acid profiles and phenotypic characteristics. Methods to obtain these characteristics and apply them to taxonomically define a bacterial species is well known in the art. In accordance with the present invention, definitive characteristics of 6 PAH-degrading isolates of “P. naphthalenovorans” are taught, and the invention is therefore contemplated to encompass all PAH-degrading isolates in the species “P. naphthalenovorans”.

[0048] The 16S rRNA gene is also an excellent indicator of genealogical relationship between species and is the most non-changing genetic marker available. The 16S ribosome gene sequences of six “P. naphthalenovorans” isolates are taught in accordance with the present invention (SEQ ID NOs:6-11). In respect to the current invention, the sequence for PR-N1 16S rRNA gene sequence (SEQ ID NO:8) is used as the type sequence for this new species. The percent homology of the 16S rRNA gene sequence for the “P. naphthalenovorans” of the invention to SEQ ID NO:8 is greater than about 95% in a preferred embodiment, greater than about 96% in a more preferred embodiment, and greater than about 97% in a most preferred embodiment. With respect to the present invention, the percent identity of 16S rRNA gene sequences is determined by the PILEUP program in the Genetics Computer Group (GCG) software package using the default parameters over the approximately 500 bp fragment generated by 27f and 1522r PCR primers.

[0049] Another way to characterize a species is through the general homology found in the genomic DNA. The percent binding (or hybridization) of one genomic DNA sample to another will give a quantitative measure of the homology between the two genomes. In regard to the current invention, the method used to determine these homologies is the S1 nuclease method (Johnson, 1994, In Methods for General and Molecular Bacteriology, pp 655-682, Gerhardt, Murry, Wood and Kreig (eds.), Washington D.C., American Society of Microbiology), and the “P. naphthalenovorans” type genome is the PR-N1 genome (ATCC Accession No. [not yet assigned]). The percent DNA binding of the “P. naphthalenovorans” of the invention to the “P. naphthalenovorans” type genome is at least 15% in a preferred embodiment, at least 40% in a more preferred embodiment, and at least 70% in a most preferred embodiment.

[0050] Fatty acid identification has been proven very useful in identifying organisms on the genus and species levels. It is a form of chemotaxonomy, and it characterizes the number and diversity of complicated biosynthetic pathways that a species possesses. By comparing the whole cell fatty acid composition of an unknown bacterium to the fatty acid compositions of type stains, the most like species of the unknown bacterium is determined. In order for these comparisons to have meaning, both all the bacteria must be grown under similar conditions. In regards to the current invention, standard growth conditions for whole cell fatty acid analysis are growth on trypticase soy agar at 28° C. for 24 hours prior to analysis. Comparisons of the fatty acids profiles are now done by computer programs with databases. Regarding the isolated bacterial cultures of the present invention, the Sherlock Microbial Identification System (Operating Manual Version 5, from MIDI, Inc., Newark, Del.) are used. A similarly index provides the degree of identity to the type strain in the MIDI library database or library databases constructed with MIDI software, with 1.0 being a perfect match. The similarity index of the “P. naphthalenovorans” of the invention to the whole cell fatty acid composition of isolate PR-N1 (Table 6) is greater than 0.4 in a preferred embodiment, greater than 0.6 in a more preferred embodiment, and greater than 0.6 in the most preferred embodiment.

[0051] The percentages of individual fatty acids may also identify a species of bacteria. A predominance of the fatty acid 15:0 anteiso is characteristic of Paenibacillus (Ash-et al., 1993, Antonie van Leeuwenhoek 64:253-260). The higher levels of 16:1 ω11c and moderate levels 17:0 anteiso fatty acids are characteristic of “Paenibacillus naphthalenovorans”. The preferred embodiments of each individual fatty acid of the species “P. naphthalenovorans” are indicated in Table 1. TABLE 1 Preferred embodiments of the percent whole cell fatty acid for each fatty acid of the “Paenibacillus naphthalenovorans”. “X” is the percent of the whole cell fatty acids on a w/w basis of the isolated “P. naphthalenovorans” of the invention. Fatty Acid Preferred More Preferred Most Preferred 14:0 iso 0.0% ≦ X ≦ 3.00% 0.0% ≦ X ≦ 2.5% 0.0% ≦ X ≦ 2.3% 14:0 2.5% ≦ X 2.5% ≦ X ≦ 6.0% 2.5% ≦ X ≦ 3.7% 15:0 iso 4.7% ≦ X ≦ 10.0% 3.0% ≦ X ≦ 6.8% 4.7% ≦ X ≦ 6.8% 15:0  35% ≦ X  45% ≦ X  45% ≦ X ≦ 55% anteiso 15:0 0.0% ≦ X ≦ 10.0% 0.0% ≦ X ≦ 5.0% 0.0% ≦ X ≦ 3.5% 16:1 0.0% ≦ X ≦ 2.5% 0.0% ≦ X ≦ 2.2% 0.0% ≦ X ≦ 1.9% ω7c alcohol 16:0 iso 0.0% ≦ X ≦ 5.9% 4.3% ≦ X ≦ 10% 4.3% ≦ X ≦ 5.9% 16:1 8.8% ≦ X 9.0% ≦ X 9.3% ≦ X ≦ 16.7% ω11c 16:0 8.5% ≦ X ≦ 20.0% 5.0% ≦ X ≦ 14.4% 8.5% ≦ X ≦ 14.4% 17:0 5.8% ≦ X ≦ 10.0% 3.5% ≦ X ≦ 7.9% 5.8% ≦ X ≦ 7.9% anteiso 17:0 iso 0.0% ≦ X ≦ 4.3% 1.7% ≦ X ≦ 5.5% 1.7% ≦ X ≦ 4.3%

[0052] Phenotypic characteristics are the most traditional of the methods used to define a species. The “P. naphthalenovorans” of the invention has a percentage of phenotypic traits of the isolate PR-N1 in Table 8 that is 80% in a preferred embodiment, 90% in a more preferred embodiment, and 95% in a most preferred embodiment.

[0053] Also provided with the current invention is a plurality of isolated bacterial strains that is useful for bioremediation. A combination of P. validus strain PR-P1, sphingomonad strain PR-P12, Arthrobacter strain PR-P3, “P. naphthalenovorans” strain PR-N5, nocardioform strain PR-N14 is taught in Example 3 as useful for degrading PAHs. In a preferred embodiment, the plurality of bacteria has at least 2 of these strains, in a more preferred embodiment at least 3 of these strains, and in a most preferred embodiment at least 4 of these strains. It is also contemplated that other isolates of these species and genera can be used in the invention. Examples of other suitable strains can be found in Tables 2-4.

[0054] Another aspect of the invention is the method to treat PAH-contaminated substrates using the isolated bacterial strains. The method of the invention comprises contacting at least one of the isolated bacterial strains of the invention to the contaminated substrate for a time sufficient to effect removal of the polyaromatic hydrocarbon.

[0055] PAH contamination is widespread and prevalent in ecosystems, but more prevalent in ecosystems associated with the marine environment. Sources of PAH contamination include industrial activities and petroleum chemical spills. Substrates suitable for treatment may be solid or liquid. Substrates may be treated in situ or removed from their location and treated elsewhere. Contaminated substrates that may be treated with the bacterial strains of the invention include, but are not limited to, harbor dredge spoils, sediments, wastewater, sea water, soil, sludge and refinery wastes. In a preferred embodiment, the substrate is dredge waste.

[0056] When substrates are not suited to the growth of the bacterial strains of the invention, the substrate may be altered in composition. In one embodiment of the method, the solid substrate is mixed with water and optionally aerated. Other contemplated amendments to the substrate include, but are not limited to various co-substrates, alternate carbon sources, emulsifiers and surfactants.

[0057] Optionally, plants may be added to the substrate before or after the bacteria is added. This embodiment is particularly advantageous for the bacterial strains that were originally isolated from the rhizosphere. As much of PAH contamination is associated with marine environments, plants that can tolerate saline conditions are particularly appropriate. Plants that are particularly suited to use with the bacterial strains of the invention for bioremediation include, but are not limited to, Spartina alterniflora, Phragmites australis, Juncus gerardi, Distichlis spicata, Sporobulus aeroides and other salt marsh grasses.

[0058] It is contemplated that the isolated bacterial strains of the invention may be used as alone or in combination with each other. Additionally, the bacterial strains of the invention may be used with other bacterial strains. Other bacterial strains that may be used in conjunction with the stains of the invention include, but are not limited to, other known PAH degraders.

[0059] The effective concentration of the bacteria in the method depends on environmental factors, PAH to be degraded, substrate and bacterial strain used. In general, the bacterial strains of the invention should be added so that their concentration on the substrate is 10⁴ to 10⁹ cells/g. Strains may be pre-induced on phenanthrene or another inducer of PA H-degrading enzymes to increase the degradation of high molecular weight PAHs. The concentration of phenanthrene for this induction may be lower than 0.01 ppm, and is likely to vary between bacterial strains. In a preferred embodiment, the concentration of phenanthrene is the lowest concentration that gives adequate induction of the bacterial strain used. The determination of this concentration is without undue experimentation and will be known to those skilled in the art of bacteriology. One experimental protocol that may be used to determine this concentration is found in Example 3.

[0060] Additionally provided with the invention is a composition for bioremediation comprising at least one of the bacterial strains of the invention and an environmentally acceptable carrier. An environmentally acceptable carrier may be such compounds as talc, among others. The bacteria may be lyophilized, hydrated or endospores. Also included in the composition may be at least one compound to aid in bioremediation. Additional compounds may enhance bacterial growth on the substrate. Such compounds include, but are not limited to, carbon sources, pH regulators, plant seeds, additional stains of bacteria, surfactants and emulsifiers. Compounds may also be added to increase the amount of PAH degradation. These compounds may affect the bacteria directly, such as with phenanthrene, or may increase the accessability of the PAHs to the bacteria, such as Tween 80. Such compounds include, but are not limited to, phenanthrene, Tween 80 and SDS.

[0061] Provided in-accordance with the present invention is a method for isolating new strains of endospore-forming bacteria with PAH-degrading properties. The method to isolate endospore-forming PAH-degrading bacterial strains comprises the steps of enriching heterogenous cultures for bacteria that can grow with PAH as the sole carbon source and screening the strains for endospore formation by killing vegetative bacteria by heat treatment. An example of this method is given in Example 1. The heat treatment can be from 70 to 90° C. for 10 to 20 minutes. Environments that are contaminated with PAHs are particular desirable for obtaining the heterogenous cultures. In a preferred embodiments, the enrichment method of Example 1 is used, and the bacterial population is enriched for isolates that can grow with naphthalene, phenanthrene or bi-phenyl as the sole carbon source. A bacterial culture which is enriched for strains that can grow with each of two or more PAHs as the sole carbon source is particularly preferred.

[0062] The aforementioned enrichment method can also be used to isolate species of endospore-forming bacteria with PAH-degrading activities that are effective against other PAHs. By using different PAHs as sole carbon sources in these cultures, bacterial isolates with a variety of PAH-degrading activities can be isolated.

[0063] With the features available in the present invention, it is also possible to the directly isolate the bacterial species of the invention using methods well known to those in the art. Standard high stringency hybridization screening of colonies using known genomic sequences of strains PR-N1 (ATCC Accession No. [not yet assigned]), PR-P1 (ATCC Accession No. [not yet assigned]), PR-N4 (ATCC Accession No. [not yet assigned]) and PR-B2 (ATCC Accession No. [not yet assigned]) as probes is also possible, and methods for these screens can be easily performed by one skilled in the art using available protocols. In preferred embodiments, a 16S rRNA gene sequence (SEQ ID NO:1-11) is used as a probe. Hybridization stringencies are use to identify related bacteria that are at least 85% homologous in a preferred embodiment, at least 94% in a more preferred embodiment, and at least 97% in a most preferred embodiment. Any of the morphological, biochemical and physiological traits that are attributed to P. validus and “P. naphthalenovorans” in the Examples may also be used as the basis of screens that are specific to PAH-degrading Bacillaceae species.

[0064] A high stringency hybridization screening can be preformed by methods that will be well known to those of skill in the art, such as methods for identifying bacterial colonies that contain recombinant plasmids (Sambrook et al., Molecular Cloning, Cold Spring Harbor Laboratory (1989), Sections 1.85-1.101 (hereinafter “Sambrook et al.”)). For example, a high stringency hybridization may be performed, according to the method of Sambrook et al. (1989, supra), using a hybridization solution comprising-: 6× SSC, 5× Denhardt's reagent, 0.5% SDS, 100 μg/ml denatured, fragmented salmon sperm DNA. Hybridization is carried out at 65° C. for at least six hours. Following hybridization, filters are washed as follows: (1) 5 minutes at room temperature in 2× SSC and 1% SDS; (2) 15 minutes at room temperature in 2× SSC and 0.1% SDS; (3) 30 minutes-1 hour at 37° C. in 1× SSC and 1% SDS; (4) 1 hour at 65° C. in 0.1× SSC and 0.5% SDS, changing the solution every 30 minutes.

[0065] One common formula for calculating the stringency conditions required to achieve hybridization between nucleic acid molecules of a specified sequence homology (Sambrook et al., 1989, supra):

T _(m)=81.5° C.+16.6Log [Na+]+0.41(% G+C)−0.63 (% formamide)−600/#bp in duplex

[0066] As an illustration of the above formula, using [N+]=[0.368] and 50% formamide, with GC content of 42% and an average probe size of 200 bases, the T_(m) is 57° C. The T_(m) of a DNA duplex decreases by 1-1.5° C. with every 1% decrease in homology. Thus, targets with greater than about 75% sequence identity would be observed using a hybridization temperature of 42° C.

[0067] The foregoing description set forth the general procedures involved in making and using the present invention. To the extent that specific materials are mentioned, it is merely for purposes of illustration and is not intended to limit the invention. Unless otherwise specified, general cloning procedures, such as those set forth in Sambrook et al., Molecular Cloning, Cold Spring Harbor Laboratory (1989) (hereinafter “Sambrook et al.”) or Ausubel et al. (eds) Current Protocols in Molecular Biology, John Wiley & Sons (1999) (hereinafter “Ausubel et al.”) are used.

[0068] The following examples are provided to describe the invention in greater detail. They are intended to illustrate, not to limit, the invention.

EXAMPLE I Isolation and Characterization of Rhizospheric PAH- and PCB-Degrading Bacteria

[0069] Plant and sediment samples. Salt marsh plant samples were obtained at two sites. The first site, considered to be pristine (uncontaminated) was at the University of Delaware Marine Station at Lewes, Del. A total of six different plant samples were collected at this site in January, 1997 and included Spartina alterniflora, Spartina patens, Distichlis spicata, Juncus gerardi, Phragmites australis, and Sporobolus aeroides. The second site was Piles Creek, a contaminated tributary of Arthur Kill located in Linden, N.J. Piles Creek was chosen for obtaining marsh plant and sediment samples based on its accessibility and contamination levels. Estuarine sediment and Spartina alterniflora plant samples were obtained at low tide from Piles Creek in February and July, 1997. The plant and sediment samples were transported on ice back to the laboratory where they were stored at 4° C. until analyzed and used for experiments.

[0070] Bacterial reference strains and media. Cultures of the following isolates were purchased from the American Type Culture Collection (Rockville, Md.) and used as controls and references in the phenotypic and whole-cell fatty acid analyses: Bacillus brevis ATCC 8246, Paenibacillus alvei ATCC 6344, Paenibacillus pabuli ATCC 43 899, Paenibacillus polymyxa ATCC 842, and Paenibacillus validus ATCC 43897.

[0071] Mineral salts basal (MSB) medium (Stanier et al., 1966, J. Gen. Microbiol. 43:159-271) was used for enrichment cultures, isolation and growth substrate tests. Solid minimal medium contained 2% noble agar (Difco Laboratories, Detroit, Mich.). Stock concentrations (100 mg ml⁻¹) of naphthalene, biphenyl and phenanthrene were dissolved in dimethyl formamide and added to liquid medium at a final concentration of 1 mg ml¹. Naphthalene and biphenyl were added in the vapor phase as crystals in the petri dish lid for solid medium. Phenanthrene was added as a 2% noble agar overlayer onto MSB agar plates at a final concentration of 1 mg ml⁻¹.

[0072] Bacterial strains were grown on trypticase soy (Beckton Dickinson & Co., Cockeysville, Md.) agar plates for various phenotypic and fatty acid methyl ester analyses. The bacteria were routinely grown aerobically at 30° C. except where indicated. Strains were maintained on minimal medium at 4° C., and long-term storage was in 50% glycerol at −80° C.

[0073] Enrichment and isolation of PAH-degrading bacterial strains. Bacterial enrichment cultures were established in 50 ml MSB medium using naphthalene, phenanthrene or biphenyl as the sole source of carbon. Plant rhizosphere and contaminated estuarine sediment were used as inoculum for the enrichment cultures. Rhizosphere samples were obtained by splitting open the plant root mass thereby exposing the inner roots which had not come in contact with sampling or storage devices. The fine interior roots were aseptically cut and collected and 1 gram of root material was added to each enrichment culture. Sediment samples were added directly to each enrichment culture using a 1 gram subsample. A total of two enrichment cultures for each substrate were established on each rhizosphere and sediment sample. One set of enrichment cultures was placed directly in a 28° C. environmental chamber and shaken at 150 rpm. The second set of enrichments was heat treated for 10 min at 80° C. before incubation to enhance isolation of spore-forming gram-positive bacteria. The cultures were monitored for the presence of microorganisms by gram staining and microscopy and subcultured into fresh MSB medium when growth was detected. After 3 to 4 subcultures, the bacteria were plated onto MSB agar plates containing the same substrate as the enrichment.

[0074] Phenotypic characterizations. PAH-degrading isolates were morphologically and phenotypically characterized and compared to type strains using; phase-contrast microscopy, whole-cell fatty acid profiles using the Sherlock Microbial Identification System (Newark, DE), API 20E and 50CH system tests (bioM rieux Vitek, Inc., Hazelwood, Mo.), starch and casein hydrolysis, and the effects of temperature, anaerobiosis and salinity on growth. In addition, the ability of several selected strains to grow on various aromatic substrates was also examined. Several of the gram-positive strains were analyzed for their ability to grow on a variety of aromatic compounds including naphthalene, phenanthrene, biphenyl, phthalate, gentisate, o-, m- and p-hydroxybenzoate, and benzoate. Naphthalene, biphenyl and phenanthrene were added to MSB agar plates as described in the section on bacterial reference strains and media. The organic acids were added to media at a final concentration of 5-10 mM and as sodium salts when necessary.

[0075] Phase-contrast microscopy was used for the morphological examination of bacterial cells. The strains to be tested were inoculated into 2 ml of trypticase soy broth (TSB) and incubated on a rotary wheel for 24 h at 28° C. The cells were examined for motility and morphology at 24, 48 and 72 h by placing a drop of culture onto 1% agarose-coated and non-coated glass slides. The agarose coating allowed for more detailed examination and photography of motile cells.

[0076] Whole-cell fatty acid analyses were performed on all of the isolates by growing the cells for 24 h on trypticase soy agar (TSA). Cellular fatty acids were extracted, methylated, and detected with a Hewlett Packard model 5890 Series II gas chromatograph and were identified using the Sherlock Microbial Identification System (Operating Manual Version 5, MIDI, Inc.) and the Aerobe (TSBA version 3.9) database. In addition, the Microbial Identification System includes cluster analysis and principle component analysis programs for establishment of relationships among strains (i.e. Euclidean distance).

[0077] Isolation and identification of PAH-degrading bacterial strains. Bacterial enrichment cultures were established on all of the Delaware plant rhizosphere samples using naphthalene as the sole source of carbon. Table 2 lists the different bacteria isolated from these plants. The low number and diversity of bacteria isolated from this site was expected due to its pristine nature. TABLE 2 Naphthalene-degrading bacteria isolated by enrichment from the rhizosphere of pristine salt marsh plants obtained at the University of Delaware Marine Station at Lewes, Delaware. Heat Bacterial Similarity Strain Treatment^(a) Plant species^(b) Identification^(c) Index^(d) Salt-N1 No Spartina alterniflora Pseudomonas 0.59 fluorescens Salt-N2 No Spartina alterniflora Pseudomonas 0.81 putida JG-N1 Yes Juncus gerardi Paenibacillus 0.80 validus JG-N2 No Juncus gerardi Paenibacillus 0.81 validus JG-N3 Yes Juncus gerardi Paenibacillus 0.87 validus DS-N1 Yes Distichlis spicata Bacillus brevis 0.45 DS-N2 No Distichlis spicata Paenibacillus 0.92 validus DS-N3 Yes Distichlis spicata Paenibacillus 0.81 validus SA-N1 Yes Sporobolus aeroides Paenibacillus 0.13 pabuli

[0078] In contrast, a total of 41 strains have been isolated from Spartina alterniflora plant and sediment samples obtained from contaminated Piles Creek in New Jersey, using either naphthalene, phenanthrene or biphenyl as the sole source of carbon (Tables 3 and 4). Heat treatment (80° C. for 10 minutes) prior to enrichment was included for each of the substrates tested in an attempt to isolate endospore-forming gram-positive bacteria. Endospore-forming bacteria able to degrade PAHs are considered more favorable for bioremediation purposes due to their ability to survive adverse environmental conditions (i.e., cold, dry). Table 3 and Table 4 list the Piles Creek isolates obtained from the sediment and rhizosphere, respectively, for each of the substrates tested. The heat treatment was successful in isolating gram-positive endospore-forming bacteria. TABLE 3 Identification of PAH-degrading bacteria isolated by enrichment from contaminated sediment collected at Piles Creek, New Jersey. Heat Strain treatment^(a) Bacterial Identification^(b) Similarity Index^(c) Naphthalene Gram-negative: PS-N2 No Pseudomonas fluorescens 0.47 PS-N4 No Pseudomonas stutzeri 0.89 PS-N5 No Pseudomonas stutzeri 0.86 Gram-positive: PS-N1 Yes Paenibacillus pabuli 0.26 PS-N6 Yes Paenibacillus validus 0.34 PS-N3 No Nocardia asteroides 0.71 Phenanthrene Gram-negative: PS-P2 No Alcaligenes xylosoxydans 0.65 Gram-positive: PS-P1 No Mvcobacterium sp. not applicable

[0079] TABLE 4 Identification of PAH-degrading bacteria isolated by enrichment from the rhizosphere of Spartina alterniflora growing in contaminated sediment at Piles Creek, New Jersey. Heat Similarity Strain treatment^(a) Bacterial Identification^(b) Index^(c) Naphthalene Gram-negative: PR-N6 No Pseudomonas chlororaphis 0.85 PR-N7 No Pseudomonas stutzeri 0.88 PR-N8 No Pseudomonas putida 0.82 PR-N9 No Pseudomonas putida 0.87 PR-NIO No Pseudomonas putida 0.82 Gram-positive: PR-NL Yes Paenibacillus alvei 0.18 PR-N2 Yes Paenibacillus pabuli 0.06 PR-N3 Yes Paenibacillus validus 0.87 PR-N4 Yes Paenzbacillus validus 0.86 PR-N5 Yes Paenibacillus pabuli 0.06 PR-N11 Yes Paenibacillus pabuli 0.06 PR-N12 Yes Paenibacillus pabuli 0.07 PR-N13 Yes Paenibacillus validus 0.81 PR-N16 Yes Paenibacillus pabuli 0.16 PR-N19 Yes Paenibacillus validus 0.93 PR-N20 Yes Paenibacillus validus 0.84 PR-N21 Yes Paenibacillus validus 0.75 PR-N22 Yes Paenibacillus validus 0.81 PR-N14 No Nocardia asteroides 0.77 PR-N15 No Nocardia brasiliensis 0.21 PR-N17 No Nocardia asteroides 0.57 PR-N18 No Nocardia asteroides 0.14 Phenanthrene Gram-negative: PR-P12 No Flavobacterium resinovorum  0.79, Gram-positive: PR-P1 Yes Paenibacillus validus 0.85 PR-P2 No Paenibacillus validus 0.90 PR-P3 No Arthrobacter oxydans 0.46 PR-P6 Yes Paenibacillus validus 0.88 PR-P9 Yes Paenibacillus validus 0.91 PR-PIO Yes Paenibacillus validus 0.91 PR-P11 Yes Paenibacillus validus 0.70 PR-P13 Yes Paenibacillus validus 0.91 Biphenyl Gram-positive: PR-B1 No Paenibacillus validus 0.87 PR-B2 No Bacillus brevis 0.34

[0080] The identification of all strains is based mainly on their fatty acid methyl ester profiles compared to the TBSA MIDI library., An excellent identification corresponds to a similarity index (SI) of >0.6 (1.0 being a perfect match), a good identification corresponds to a SI of 0.4-0.6 and a poor identification corresponds to a SI<0.4. All of-the Delaware isolates have a good to excellent identification except for strain SA-N1 isolated from Sporobolus aeroides. This strain has a unique colony morphology (white, highly mucoid) compared to the other gram-positive spore-forming Delaware isolates. Similarly, the gram-positive spore-forming strains exhibiting the lowest similarity index obtained from Piles Creek sediment and rhizosphere samples also share this colony morphology.

[0081] A pairwise comparison Euclidean distance dendrogram based on whole-cell fatty acid compositions of the sediment and rhizosphere PAH-degrading isolates was constructed (FIG. 1). The dendrogram provides information about samples that are clustered. For example, samples that are joined at lower levels of the dendrogram are more closely related than those that are joined at higher levels. A Euclidean Distance of 10 or less may be considered to be the same species, 6 or less the same subspecies and 2.5 or less as two different runs of the same strain. The isolates fall within three main groups (FIG. 1). Group I includes the endospore-forming gram-positive bacteria. Group 2 includes the gram-positive Nocardioforms and Group 3 includes the gram-negative Pseudomonads.

[0082] Phenotypic characterizations. Among all of the isolates, the gram-positive isolates were able to degrade a wider range of polyaromatic hydrocarbons than the gram-negative Pseudomonad isolates. In particular, while none of the tested isolates could metabolize pyrene well, the gram-positive isolates were more effective in general than the gram-positive species at metabolizing phenanthrene, fluorene and naphthalene. Among the gram-positive isolates, the spore-forming isolate was very effective at metabolizing naphthalene, biphenyl, fluorene and phenanthrene while the nonspore-forming gram-positive isolates where less-effective at metabolizing biphenyl, fluorene and phenanthrene (Table 5). TABLE 5 Ability of several isolated to utilize a variety of polyaromatic hydrocarbons. % PAH remaining^(b) Naphtha- Phenan- Strain lene Biphenyl Fluorene threne Pyrene Pseudomonads PR-N7 0 85 100 85 90 PR-N6 0 69 78 71 90 PR-N10 40 90 97 89 100 PS-P2a 44 51 79 28 100 Gram-positive Non-sporeformers PR-N15 0 84 80 68 100 PR-P3 0 84 42 1 100 Sporeformer PR-P1 0 0 29 8 100

EXAMPLE 2 Characterization of Spore-Forming Gram-Positive Strains

[0083] Due to the novelty of gram-positive endospore-forming bacteria which are able to degrade PAHs, these particular isolates where characterized further. The spore forming gram-positive isolates exhibited two major colony morphologies, mucoid and nonmucoid, when grown on solid media. A mucoid colony morphology is characterized by a slimy or gummy appearance while a nonmucoid colony morphology is characterized by a smooth clear gray appearance. Phase contrast microscopy showed that all the strains were motile and illustrated typical vegetative-spore-forming life cycle. TABLE 6 Whole cell fatty acid comparisons of P. validus (ATCC 43897) and the PAH-degrading Paenibacillus isolated as determined by gas chromatograph analysis of their methyl esters. Fatty acid (%, w/w of total)^(a) Strain 14:0 1SO 14:0 15:0 iso 15:0 anteiso 15:0 16:1 ω7c alcohol 16:0 1SO 16:1 ω11c 16:0 17:0 anteiso 17:0 1SO Group 1 (Mucoid colony morpology) PR-N1 PS-N1 PS-N6 SA-N1 PR-N16 PR-N5 0.0 2.3 1.8 1.9 1.3 0.0 2.5 2.8 2.8 2.8 2.7 3.7

51.8 55.0 52.9 49.8 45.4 47.9 0.0 1.5 1.5 # 2.1 3.5 0.0 0.0 0.0 1.9 1.5 1.0 0.0 5.6 5.5 5.9 5.2 4.7 4.3

7.9 6.3 5.8 6.5 6.1 6.5 3.2 1.9 1.7 2.9 4.3 2.8 Group 2 (Nonmucoid colony morphology) PR-B2 DS-N3 JG-N2 DS-N2 DS-N1 PR-P13 PR-P10 PR-P9 PR-N21 PR-N22 PR-P1 PR-P11 PR-N19 PR-N13 P. validus 3.1 2.8 3.9 3.7 2.7 2.6 2.9 2.9 3.0 # 3.3 3.4 3.4 2.9 2.6 2.7 1.4 1.3 1.8 1.7 1.3 2.1 1.9 1.7 1.3 1.5 1.7 3.1 1.6 1.4 1.8

48.1 48.9 49.4 50.7 50.6 49.1 # 49.0 46.3 53.9 53.2 54.0 51.0 50.7 52.3 48.0 0.6 0.7 0.7 0.9 0.8 0.8 0.6 1.0 0.0 0.0 0.8 1.4 1.0 1.0 0.9 2.5 3.1 3.1 2.8 # 2.9 2.2 3.7 3.1 2.7 2.9 3.2 2.5 2.3 1.7 2.2 9.1 7.0 8.1 7.0 6.8 6.5 6.2 7.5 7.3 7.4 6.6 5.7 8.3 7.9 6.8

4.9 # 5.0 3.8 4.3 4.7 4.7 4.8 5.1 4.7 4.8 4.4 4.1 5.1 5.7 5.3 5.3 4.8 3.4 3.3 4.0 4.2 3.0 4.2 3.5 3.5 3.0 1.6 3.4 4.3 # 4.3

[0084] Fatty acid methyl ester analysis (FAME, as described in Example 1) determined that the nonmucoid as well as mucoid isolates were members of the genus Paenibacillus, formerly part of the genus Bacillus (Ash et al., 1993, Antonie van Leeuwenhoek 64:253-260). The predominant fatty acids were 15:0 anteiso (45.4-55.0% of total), 15:0, 16:0 iso, 16:0 and 16:1 ω11c (Table 6). The high percentage-of 15:0 anteiso fatty acids is a characteristic of the genus Paenibacillus. The mucoid and nonmucoid strains can be distinguished by their 10:0 iso, 16:1 ω11c and 16:0 fatty acid composition (Table 6).

[0085] A dendrogram was constructed containing only these bacteria and ATCC type strains reveals that the isolates fall within two groups, the non-identified Paenibacillus-like bacteria (Group 1) and the Paenibacillus validus cluster (Group 2) (FIG. 2). The non-identified group all have low similarity indexes to the MIDI library (Table 7). This group also has a distinct white to grey mucoid colony morphology compared to the Paenibacillus validus group which have a smooth clear tan to grey mottled appearance and do not exhibit a mucoid quality.

[0086] The gram-positive endospore-forming strains and ATTC type strains were also used for examination using principal component analysis (FIG. 3). The two-dimensional plot shows that all of the PAH-degrading isolates are different from the Paenibacillus and Bacillus type strains tested. One cluster of strains (Paenibacillus validus group) is bordered by Paenibacillus validus and Paenibacillus alvei, but the isolates are clearly distinct from these strains. The second group which includes the unidentified Paenibacillus-like bacteria which exhibit a white-mucoid colony morphology. TABLE 7 Comparison of bacterial identification using FAME and partial 16S rRNA gene sequences of the PAH-degrading Paenibacillus strains isolated from the sediment and Rhizosphere of salt marsh plants. Fatty acid methyl ester Partial 16S rRNA gene sequence^(b) analysis^(a) % Simi- Homology larity to Strain Identification Index Closest Match P. validus Group 1 (Mucoid colony morphology) PS-N1 Paenibacillus alvei 0.261 Paenibacillus validus 93 PR-N1 Paenibacillus pabuli 0.181 Paenibacillus validus 94 PS-N6 Paenibacillus 0.334 Paenibacillus validus 95 validus ^(c) PR-N5 Paenibacillus pabuli 0.059 Paenibacillus validus 93 PR-N16 Paenibacillus pabuli 0.155 Paenibacillus validus 93 SA-N1 Paenibacillus pabuli 0.129 Paenibacillus validus 93 Group 2 (Nonmucoid colony morphology) PR-B2 Brevibacillus brevis 0.340 Paenibacillus validus 97 DS-N3 Paenibacillus 0.812 Paenibacillus validus 95 validus DS-N1 Brevibacillus 0.454 Paenibacillus validus 98 brevis PR-P13 Paenibacillus 0.911 Paenibacillus validus 97 validus PR-P10 Paenibacillus 0.910 Paenibacillus validus 96 validus PR-P9 Paenibacillus 0.909 Paenibacillus validus 96 validus PR-N19 Paenibacillus 0.927 Paenibacillus validus 98 validus PR-N21 Paenibacillus 0.745 Paenibacillus validus 95 validus PR-P1 Paenibacillus 0.849 Paenibacillus validus 97 validus PR-P11 Paenibacillus 0.701 Paenibacillus validus 96 validus

[0087] Biochemical characterization using the API 20E and 50CH test systems could distinguish between the two test groups of Paenibacillus, the novel mucoid strain and the nonmucoid strains including the P. validus ATCC accession strain (Table 8). The mucoid strains were positive while the nonmucoid strains were negative for the Voges-Proskauer test, the production of acetoin, and intermediate in butanediol fermentation. The mucoid strains were all unable to hydrolyze esculin, while the nonmucoid strains in general had this ability. The mucoid strains did not produce acid from glycerol, ribose, D-xylose, ducitol, inositol, amidon and glycogen while the nonmucoid strains in general could produce acid by metabolizing these compounds. Other more general differences between these two groups can be seen Table 8, for example in L-sorbose, cellobiose, D-raffinose, xylitol and β-gentiobiose metabolization.

[0088] The group 2, nonmucoid Paenibacillus strains were able to utilize a greater number of aromatic substrates that the mucoid Paenibacillus (Table 9). The nonmucoid Paenibacillus strains, in general, were able to utilize naphthalene, phenanthrene, biphenyl, p-hydroxybenzoate and benzoate, while the mucoid Paenibacillus strains could utilize naphthalene, m-hydroxybenzoate, p-hydroxybenzoate and benzoate. The ability of two of the three strains of the mucoid Paenibacillus strains to utilize m-hydroxybenzoate and the inability of all three of the mucoid Paenibacillus strains to utilize phenanthrene and biphenyl distinguishes them from the nonmucoid Paenibacillus strains tested. TABLE 8 Phenotypic characteristics of PAH degrading strains isolated from sediment and rhizosphere. Group 1 Group 2 (Mucoid morphology) (Nonmucoid morphology) Characteristics PS-N1 PR-N1 PS-N6 PR-N5 PR-N16 SA-N1 DS-N1 PR-N20 PR-N22 PR-P1 PR-P13 PR-P9 P. validus Hydrolysis of: + − − + − + + + + + nd^(b) nd + Starch API 20E Tests^(c): Citrate − − + − + − − − − − − − − Urease + + + + + + + − + + + + + Voges-Proskauer + + + + + + − − − − − − − Nitrate reduction − − − + − − − − − − − − − API 5OCH Tests^(d): Esculin hydrolysis − − − − − − + − + + + + + Acid produced: Glycerol − − − − − − + − + + + + + D-Arabinose − − − − − − − − − + − − − Ribose − − − − − − + − + + + + + D-Xylose − − − − − − + − + + + + + D-Fructose + + − + − + + − + + + + + D-Mannose + + + + + + + − − + + + + L-Sorbose + + − + + + − − − − − − − Dulcitol − − − − − − + − + + + + − Inositol − − − − − − + − + + + + + Sorbitol + − − − − − − − − − − − − ⊕ Methyl-D + + − + + + + − + + + + + glucoside Cellobiose − − − − + − + − + − − + + Melibose − − − + − + + − − + − − + D-Raffinose − − − − − − + − − + − − + Amidon − − − − − − + − + + + + + Glycogen − − − − − − + + + + + + + Xylitol + + − + − + − − − − − − − β-Gentiobiose − − − − − − + − + − − + − D-Turanose + + − + + + + + + + + + + D-Tagatose − − − − − − − − − + − + − D-Arabitol − − − − − − − + − − − + −

[0089] TABLE 9 Growth of isolates from sediment and rhizosphere on aromatic substrates. PAH-degrading Paenibacillus species Mucoid colony Non-mucoid colony morphology morphology Substrate PS-N1 PR-N1 PR-N5 PR-N4 PR-P1 PR-B2 Naphthalene + + + + + + Phenanthrene − − − + + − Biphenyl − − − + + + Phthalate − − − − − − Gentisate − − − − − − o-Hydroxy- − − − − − − benzoate m-Hydroxy- − + + − − nd benzoate p-Hydroxy- − + + + + nd benzoate Benzoate + + + + + +

[0090] The mean base composition of nuclear DNA, as indicated by mol % G+C content, is characteristic of a species. The G+C content of the mucoid and nonmucoid group was 49 and 51 mol %, respectively, but the ranges of the two groups overlapped (Table 10).

[0091] Restriction enzyme digestion patterns of genomic DNA from the Paenibacillus strains was performed to determine how many distinct strains were present. EcoR1 digests of the genomic DNA were run on a 0.8% agarose gel and the sizes of the resulting bands compared. These strains are indicated in FIG. 2 in bold type face.

[0092] DNA-DNA hybridization experiments can provide semi-quantitative data about the degree of genetic homology between different strains of bacteria. The DNA-DNA hybridization experiment with genomic DNA from the mucoid, nonmucoid and P. validus strains showed only 6% binding of DNA of the mucoid strain, PR-N1, to that of P. validus, while the DNA of PR-N1 showed high percentages of binding to that of the other nonmucoid strains, from 45.5% to 97.0%. Likewise, the degree of binding of P. validus DNA to that of the nonmucoid strains is 72.2% to 79.0%, and 13.2% to that of the mucoid strain PR-N1 (Table 10). TABLE 10 G + C contents of and DNA binding data for PAH-degrading Paenibacillus strains. % DNA binding^(a) Strain G + C content^(b) (mol %) PR-N1 P. validus Group 1 (Mucoid colony morphology) PR-N1 46.6 100 13.2 PS-N1 51.5 97.0 PR-N5 50.1 87.6 PR-N16 49.9 87.3 PS-N6 47.7 70.9 SA-N1 47.3 45.5 Group 2 (Nonmucoid colony morphology) PR-N19 50.1 79.0 PR-P1 53.0 72.2 DS-N1 48.8 PR-P9 48.8 P. validus 48.7 6.0 100 ATCC 43897

[0093] Southern hybridizations using the classical genes for naphthalene degradation, pyrene degradation and phenanthrene degradation were performed with genomic DNA from the nonmucoid Paenibacillus strains. Southern hybridizations were performed as recommended by the supplier of the nylon membrane used for hybridization (Biorad). Prehybridization and hybridization were performed at 37° C. Following hybridization, the nylon membrane was washed under low stringency condition (0.1× SSC and 0.1% SDS) at room temperature. EcoR1-digested genomic DNA was probed under low stringency conditions (Goyal and Zyistra 1996, Appl. Environ. Microbiol. 62:230-236) with a 3.5 SalI fragment from Pseudomonas putida NCIB-9816-4 (Genbank Accession No. U49496) containing the genes for naphthalene dioxygenase. No genes homologous to the Pseudomonas putida nah gene were found indicating the PAH-degrading genes from Paenibacillus are novel. Likewise, when genes from pyrene-degrading Mycobacterium sp. PY01 (supplied by G. Zylstra) and a phenanthrene-degrading Comamonas testosteroni strain (Goyal and Zylstra, J. Ind. Microbiol. Biotechnol. 1997, 19:401-407 and Goyal and Zylestra, 1996, Applied Environ. Microbic. 1996, 62:230-236) were used to probe Paenibacillus genomic DNA, no homology was found. It is therefore likely that the nonmucoid strains of Paenibacillus isolated have novel genes for naphthalene degradation, pyrene degradation and phenanthrene degradation.

[0094] Sequence analyses of 16S rRNA genes were performed on the gram-positive isolates by amplifying the 16S rRNA genes by the polymerase chain reaction (PCR) using the primers 27f and 1522r. The amplified PCR products were purified using the QIA quick PCR purification kit (QIAGEN) according to the manufacturer Ts instructions. DNA sequences were determined directly from the purified PCR products with automated fluorescent Taq cycle sequencing using the API Catalyst 800 and ABI 373A Sequencer (Applied Blosystems, Forester City, Calif.). Approximately 100 ng of the purified DNA is used for one automated fluorescent sequencing reaction. The primers for sequencing were 27f, 704f, 926f, 1242f, 321r, 685r, 907r, 1220r and 1522r (Johnson, 1994, In Methods for General and Molecular Bacteriology, pp. 683-700. Gerhardt, Murray, Wood & Krieg, eds. Washington, D.C.: American Society for Microbiology). Partial rRNA sequences for nonmucoid strains DS-N1, PR-B2, PR-N19, PR-P9 and PR-P1 are presented in SEQ ID NOs:1-5, respectively, and mucoid strains SA-N1, PS-N6, PR-N1, PR-N16, PR-N5 and PS-N1 are presented as SEQ ID NOs:6-11.

[0095] The 16s rRNA gene sequences were Blast searched for preliminary identification. Detailed gene database searching was performed in the EMBL Data Library. Multiple sequence alignment was done with the PILEUP program in the Genetics Computer Group (GCG) software package using the default parameters. The alignment was edited for the appropriate analysis by using the SUBALIGN and GDE programs from the Ribosomal Database Project (RDP). The phylogenetic analyses were performed with the PHYLIP 3.5 program (Felsenstein, 1989, Cladistics 5:164-166). Kimura's method was used to calculate evolutionary distances (Kimura, 1980, J Mol Evol 16:111-120), from which a phylogenetic dendrogram is drawn by using neighbor-joining analysis (Saitou and Nei, 1987, Mol Biol Evol 4:406-425). The SEQBOOT program was used to obtain confidence levels for neighbor-joining analysis (Felsenstein, 1985, Evolution 39:783-791).

[0096] 16S rRNA gene sequence analysis of isolated from the mucoid group and the nonmucoid group revealed low (˜94%) and high (˜98%) homology to P. validus, respectively (Table 7). In addition, a phylogenetic tree revealed that the nonmucoid group clustered within the species P. validus while the mucoid group formed a distinct cluster of Paenibacillus (FIG. 4).

[0097] The strains can be classified into two species, Paenibacillus validus and a new species of Paenibacillus.

EXAMPLE III The use of PAH-Degrading Strains for Bioremediation

[0098] The degradation of PAHs, most notably phenanthrene and pyrene, was observed in the sediment slurries with and without Spartina alterniflora.

[0099] A. Microbial Decontamination of Liquid Culture

[0100] Liquid culture decontamination. The ability of Paenibacillus strain PR-P1 to degrade PAHs was determined in liquid culture media. Fifty ml serum vials were filled with 10 ml MSB (minimal salts broth) each, final volume. All vials additionally contained 1 ppm of a 4-ring PAH and 10⁵ cells/ml. The 4-ring PAHs used were pyrene, benz[a]anthracene and fluoranthene. Specific treatments additionally comprised 10 ppm phenanthrene or 10 ppm salicylate. Vials with culture were incubated at 28° C. with 200 RPM shaking. Triplicate cultures were sacrificed at days 0, 3, 5 and 7, and analyzed for PAHs.

[0101] Extraction and analysis of PAHs. One gram of sample is put into a 7 ml extraction vial. An internal standard (2-methylnaphthalene) is added at a final concentration of 20 ppm and the vial is shaken overnight with 2 ml hexane and 1 ml acetone. The extract is centrifuged at 2,000 RPM for 5 min. and the organic phase removed to a new extraction vial. The remaining material is further extracted with 1 ml hexane for 4 hours, after with it is centrifuges and the organic phases combined. The extract is analyzed for PAH content using a Hewlett Packard 5890 Series II Gas Chromatograph equipped with a HP-5MS column cross-linked with 5% Ph ME siloxane and a 5971 Series mass selective detector.

[0102] A pure culture of Paenibacillus validus strain PR-P1 degraded fluoranthene and pyrene only in the presence of phenanthrene (FIG. 5), indicating that phenanthrene stimulated the co-metabolic utilization of fluoranthene and pyrene. At three days, the treatment containing phenanthrene showed 83% loss of fluoranthene and 20% loss of pyrene. At seven days, 86% loss of fluoranthene and 27% loss of pyrene was observed.

[0103] The ability of a consortium of bacteria to degrade PAHs was also determined in liquid culture. The bacterial consortium consisted of Paenibacillus strain PR-P1, sphingomonad strain PR-P12, and Arthrobacter strain PR-P3, each inoculated at 108 cells/ml and Paenibacillus strain PR-NS and nocardioform strain PR-N14, each inoculated at 104 cells/ml. Treatments of either 10 ppm salicylate or 13 ppm Tween-80 alone with “killed inoculum” and a “no inoculum” control were examined. Culture vials were incubated at 28° C. with 200 RPM shaking. Triplicate cultures were sacrificed, extracted with acetone:hexane (2:1) and analyzed by GC/MS with a 2-methylnaphthalene internal standard.

[0104] The consortium of bacteria degraded fluoranthene, pyrene and benz[a]anthracene in the presence of phenanthrene, salicylate and Tween-80 at similar rates (FIG. 6).

[0105] B. Plant-Microbial Decontamination of Dredge Material

[0106] Plants and plant-associated bacteria were used in the first system to remediate PAH-contaminated dredge material. Spartina alterniflora was chosen as the plant species due to its ease of greenhouse propagation and ability to grow in-dredge material. The rhizosphere-associated phenanthrene-degrading strains PR-P1 (P. validus) and PR-P3 (Arthrobacter) were chosen as inocula due to their ability to produce spores (PR-P1) and growth on various aromatic substrates (see Table 5). The experiment was performed in triplicate using spiked and non-spiked dredge material for each of the treatments.

[0107] Approximately 400 ml of dredge material, obtained from Newtown Creek, was placed into 600 ml glass beakers. Half of the beakers containing dredge material were spiked with a mixture of PAHs dissolved in acetone. The mixture contained a mixture of 2-, 3- and 4-ringed PAHs including naphthalene, biphenyl, fluorene, phenanthrene and pyrene. Spiking the dredge material was required to determine the ability of the strains and plants to fully remediate a highly polluted sediment. Spiked treatments were mixed thoroughly with a concentrated acetone PAH-mixture to give a final concentration of 100 ppm for each compound before the addition of bacteria and plants.

[0108] The bacterial strains were grown to mid-to-late log phase in TSB (tryptic soy broth) and harvested by centrifugation at 5,000 rpm for 10 min. The cells were washed and pelleted by centrifugation twice and washed with a mineral salts medium. The washed cells were diluted into {fraction (1/10)} minimal salts solution and added to the appropriate treatment where they were mixed to a final concentration of approximately 10⁷ cells ml⁻¹ for high density inoculation and 10⁵ cells ml⁻¹ for low density inoculation. For treatments receiving plants, one S. alterniflora plant (ca. 20-24 in.) was placed in the center of an appropriate beaker by pushing the plant root through the soft dredge material. Each beaker was then flooded with approximately 2 inches of tap water to simulate an estuarine environment and also to stimulate plant growth.

[0109] Samples of dredge material for PAH determination and bacterial analyses were obtained at time 0 and at 7 day intervals by plunging a cut 1 cc syringe barrel to the bottom of the beaker and slowly filling the barrel with dredge material as the syringe was pulled out of the beaker. The samples were obtained at random areas within the beakers. For PAH analyses, 2 ml was taken from each treatment and time point and frozen (−20° C.) until extracted. PAH extraction and analysis was performed an aforementioned.

[0110] A 1 ml dredge sample was obtained for bacterial analyses for days 0 and 14 only. Bacterial cells were extracted from the dredge material by vortexing with 10 ml of 0.01 M phosphate buffer saline (pH 7.0) containing 0.03% Tween 80 (PBS-T). The bacterial extracts were diluted in PBS-T and plated onto MSB agar plates containing an over-saturated solution of phenanthrene as an agar overlay, and also onto MSB agar plates in which naphthalene was added in the vapor phase as crystals in the petri dish lid. The plates were incubated at 30° C. and examined at 1 and 2 weeks for determination of the number of colony forming units (CFU) per g dredge material.

[0111] Analyses of extracts from selected treatments of the small-scale plant-microbial decontamination experiment revealed little to no degradation of the added PAHs. While not the only explanation, the slow rate of degradation may be due to the highly anaerobic nature of the dredge material. The plant-microbial system may therefore be too anaerobic for a feasible and economic time frame for decontamination of dredge material. It is however very likely that this method will be successful if soil is used rather than dredge material. As the bacteria used were isolated from the rhizosphere of Spartina alterniflora, their growth is likely to be optimal in this environment. It is significant however that the greenhouse-propagated Spartina alterniflora plants were able to live and grow in the contaminated dredge material, and therefore this plant suitable for bioremediation efforts.

[0112] C. Microbial Decontamination of Dredge Material Using an Aerobic Slurry System.

[0113] A second remediation system for dredge material was devised that used dredge material that had been aerated and mixed with an equal volume of water. This aerobic microbial-slurry model system was designed to determine the rate and extent of microbial degradation of a contaminated dredge-slurry.

[0114] For this experiment, approximately equal volumes (500 ml) of dredge material and water were mixed under forced aeration for 1 week prior to bacterial inoculation of slurry microcosms. The microcosms consisted of 50 ml glass serum bottles containing 5 ml of aerated slurry. The degradation experiment was performed in triplicate for each treatment using slurry spiked with PAHs to a final concentration of 50 ppm. The PAHs were added to each individual serum bottle from a concentrated acetone-cocktail as described in the plant-microbe decontamination system. The treatments consisted of sterile and non-sterile slurry, non-sterile slurry+PR-P1 (at 10⁹, 10⁷ and 10⁵ cells ml⁻¹) and non-sterile slurry+PR-P3 (at 10⁹, 10⁷ and 10⁵ cells ml⁻¹). In addition, 3 treatments using MSB rather than slurry was used to determine the ability of bacterial isolates to degrade a mixture of PAHs in a defined medium versus sediment. These treatments were also spiked with PAHs at a final concentration of 50 ppm and consisted of 5 ml of MSB, MSB+PR-P1 (10⁷ cells ml⁻¹) and MSB+PR-P3 (10⁷ cells ml⁻¹). All the bottles were Teflon-stoppered through which an 18 gauge cotton-plugged needle was pierced. The microcosms were then placed in a 30° C. environmental chamber at 90 rpm.

[0115] Sampling for PAH analyses were performed at 8 time points ranging from day 0 to day 49 (7 day sampling interval). The microcosms were frozen at −20° C. until extracted for GC/MS. For PAH analyses, the content of the entire slurry system was extracted overnight with 4 ml hexane and 2 ml acetone by shaking at 200 rpm. The serum bottles were then centrifuged for 5 min at 1,500 rpm and the organic phase was removed to a fresh 7 ml extraction vial. The slurry was further extracted using 2 ml hexane for 4 hours by shaking at 200 rpm. The bottles were centrifuged and the organic phases were combined and analyzed by GC/MS as described above.

[0116] Uninoculated and inoculated sediment slurries both showed loss of the 2- and 3-ringed PAH, naphthalene, biphenyl, fluorene and phenanthrene. However, pyrene degradation was only observed in PR-P1 inoculated treatments.

[0117] The present invention is not limited to the embodiments described and exemplified above, but is capable of variation and modification without departure from the scope of the appended claims.

1 11 1 1130 DNA Paenibacillus validus misc_feature (79)..(79) n=a, c, g or t 1 ttagagtttg atcctggctc aggacgaacg ctggcggcgt gcctaataca tgcaagtcga 60 gcggacttat ccttcgggnt nggttagcgg cggacgggtg agtaacacgt aggcaacctg 120 cctgtaagat cgggataact accggaaacg gtagctaaga ccggatagct ggtttctccg 180 catgggggaa tcatgaaaca nggggcaacc tgtggcttac ggatgggcct gcggcgcatt 240 agctagttgg tggggtaacg gcccaccaag gcgacgatgc gtagccgacc tgagagggtg 300 atcggccaca ctgggactga gacacggccc agactcctac gggaggcagc agtagaggaa 360 tctttccgca atgggcgcaa gcctgacgga gcaacgccgc gtgagtgatg aaggttttcg 420 gatcgtaaag ctctgttgcc aaggaagaac gcctcggaga gtaactgctc tgagggtgac 480 ggtacttgag aagaaagccc cggctaacta cgtgccagca gccgcggtaa tacgtagggg 540 gcaagcgttg tccggaatta ttgggcgtaa agcgcgcgca ggcggtcttt taagtttggt 600 gtttaagccc ggggctcaac cccggttcgc actgaaaact gggagacttg agtgcaggag 660 aggaaagcgg aattccacgt gtagcggtga aatgcgtaga gatgtggagg aacaccagtg 720 gcgaaggcgg ctttctggac tgtaactgac gctgaggcgc gaaagcgtgg ggagcaaaca 780 ggattanata ccctggtagt ccacgccgta aacgatgagt gctaggtgtt aggggtttcg 840 atacccttgg tgccgaagta aacacaataa gcactccgcc tggggagtac gctcgcaaga 900 gtgaaactca aaggaattga cggggacccg cacaagcagt ggagtatgtg gtttaattcg 960 aagcaacgcg aagaacctta ccaggtcttg acatccctct gaccggtaca gagatgtacc 1020 ttnccttcgg ggcagaggag acaggtggtg catggttgtc gtcagctcgt gtcgtgagat 1080 gttgggttaa gtcccgcaac gagcgcaacc cttgaactta gttgccagca 1130 2 1641 DNA Paenibacillus validus misc_feature (12)..(12) n=a, c, g or t 2 ctttgggcaa angaancnng tngtgcangg ttgttgtcag ntngtgtngn taaangntng 60 gttnagtncc gcnacgaggg caacccttna anttagntgc caannnttna gttgggcact 120 ctaagttgac tgccggtgac aaaccggagg aaggtgggga tgacgtcaaa tcatcatgcc 180 ccttatgacc tgggctacac acgtactaca atggccggta caacgggaag cgaagtcgcg 240 agatggagcg aatccttaga agccggtctc agttcggatt gcaggctgca actcgcctgc 300 atgaagtcgg aattgctagt aatcgcggat cagcatgccg cggtgaatac gttcccgggt 360 cttgtacaca ccgcccgtca caccacgaga gtttacaaca cccgaagtcg gtggggtaac 420 cgcaaggagc cagccgccga aggtggggta gatgattggg gtgaagtcgt aacaaggtag 480 ccgtaatack gcaaggtscr gctggactca cctccttgcg gccgcccaat ggttagcggc 540 ggacgggtga gtaacacgta ggcaacctgc ctgtaagatc gggataacta ccggaaacgg 600 tagctaagac cggatagctg gtttctccgc atgggggaat catgaaacat ggggcaacct 660 atggcttacg gatgggcctg cggcgcatta gctagttggt ggggtaatgg cccaccaagg 720 cgacgatgcg tagccracct gagagggtga tcggccacac tgggactgar acacggccca 780 ractcctacg ggaggcagca gtagggaatc ttccgcaatg ggcgcaagcc tgacggaaca 840 acgccgcgtg agtgatgaag gttttcggat cgtaaagctc tgttgccaag gaagaacgcc 900 tcggagagta actgctctga gggtgacggt acttgagaag aaagccccgg ctaactacgt 960 gccagcagcc gcggtaatac gtagggggca agcgttgtcc ggaattattg ggcgtaaagc 1020 gcgcgcaggc ggtcttttaa gtttggtgtt taagcccggg gctcaacccc ggttcgcact 1080 gaaaactggg agacttgagt gcaggacagg aaacangaat tacanggtgt ancncagaaa 1140 agtgngannt gtgtatgaac accagtgncg aagncacttg ctttctgaga ctgtaactga 1200 cgacattgag gcgckaaagc gtggggagca aacaggatta nataccctgg tagtccacgc 1260 cgtaaacgat gagtgctagg tgttaggggt ttcgataccc ttggtgccga agtaaacaca 1320 ataagcactc cgcctgggga gtacgctcgc aagagtgaaa ctcaaaggaa ttgacgggga 1380 cccgcacaag cagnggagta tgtggnttaa ttngaagcaa cgcgaaaaac cttaccaggt 1440 cttgacatcc ctctgaccgg tacanagatt gtacctttcc ttcggggcan agganacagg 1500 tggtgcatgg ttgtcntcag cttgtgtcgt nagatgttgg gttaantccg caaccgagcn 1560 caacccttna aacttagttt ccaacanttt atttngccnc tttaacttnc nttgtcnnnn 1620 ccnaaccggn tggaagnngg g 1641 3 1431 DNA Paenibacillus validus misc_feature (66)..(66) n=a, c, g or t 3 tagagtttga tcctggctca ggacgaacgc tggcggcgtg cctaatacat gcaagtcgag 60 cggacntnnt ccttcgggaa tggttagcgg cggacgggtg agtaacacgt aggcaacctg 120 cctgtaagat cgggataact accggaaacg gtagctaaga ccggatagct ggtttctccg 180 catgggggaa tcatgaaaca cggggcaacc tgtggcttac ggatgggcct gcggcgcatt 240 agctagttgg tggggtaawg gcccaccaag gcgacgatgc gtagccgacc tgagagggtg 300 atcggccaca ctgggactga gacacggccc agactcctac gggaggcagc agtagggaat 360 cttccgcaat gggcgcaagc ctgacggagc aacgccgcgt gagtgatgaa ggttttcgga 420 tcgtaaagct ctgttgccaa ggaagaacgc ctcggagagt aactgctctg agggtgacgg 480 tacttgagaa gaaagccccg gctaactacg tgccagcagc cgcggtaata cgtagggggc 540 aagcgttgtc cggaattatt gggcgtaaag cgcgcgcagg cggtctttta agtttggtgt 600 ttaagcccgg ggctcaaccc cggttcgcac tgaaaactgg gagacttgag tgcaggagag 660 gaaagcggaa ttccacgtgt agcggtgaaa tgcgtagaga tgtggaggaa caccagtggc 720 gaaggcggct ttctggactg taactgacgc tgaggcgcga aagcgtgggg agcaaacagg 780 attagatacc ctggtagtcc acgccgtaaa cgatgagtgc taggtgttag gggtttcgat 840 acccttggtg ccgaagtaaa cacaataagc actccgcctg gggagtacgc tcgcaacgag 900 tgaaactcaa aggaattgac ggggacccgc acaagcagtg gacgtatgtg gtttaattcg 960 aagcaacgcg aagaacctta ccaggtcttg acatccctct gaccggtaca gagatgtacc 1020 ttcccttcgg ggcagaggag acaggtggtg catggttgtc gtcagctcgt gtcgtgagat 1080 gttgggttaa gtcccgcaac gagcgcaacc cttgaactta gttgccaagg caagaacgcc 1140 tcggagagta actgctctga gggtgacggt acttgagaag aaagccccgg ctaactacgt 1200 gccagcagcc gcggtaatac gtagggggca agcgttgtcc ggaattattg ggcgtaaagc 1260 gcgcgcaggc ggtcttttaa gtttggtgtt taagcccggg gctcaacccc ggttcgcact 1320 gaaaactggg agacttgant gcangacang antcccgaat tccccctgtn tccggtnaaa 1380 tncctncaca tntggatgac tccccntngc tacggcggcc ttctggaccc t 1431 4 1567 DNA Paenibacillus validus misc_feature (40)..(40) n=a, c, g or t 4 agtttgatag agtttgatcc tggctcagga cgaacgctgn cggcgtgcct aatacatgca 60 agtcgagcgn acttatcctt cgggataggt tagcggcgga cgggtgagta acacgtaggc 120 aacctgcctg taagatcggg ataactaccg gaaacggtag ctaagaccgg atagctggtt 180 tctccgcatg ggggaatcat gaaacatggg gcaacctgtg gcttacggat gggcctgcgg 240 cgcattagct agttggtggg gtaatggccc accaaggcga cgatgcgtag ccgacctgag 300 agggtgatcg gccacactgg gactgagaca cggcccarac tcctacggga ggcagcagta 360 gggaatcttc cgcaatgggc gcaagcctga cggagcaacg ccgcgtgagt gatgaaggtt 420 ttcggatcgt aaagctctgt tgccaaggaa gaacgcctcg gagagtaact gctctgaggg 480 tgacggtact tgagaagaaa gccccggcta actacgtgcc agcagccgcg gtaatacgta 540 gggggcaagc gttgtccgga attattgggc gtaaagcgcg cgcaggcggt cttttaagtt 600 tggtgtttaa gcccggggct caaccccggt tcgcactgaa aactgggaga cttgagtgca 660 ggagaggaaa gcggaattcc acgtgtagcg gtgaaatgcg tagagatgtg gaggaacacc 720 agtggcgaag gcggctttct ggactgtaac tgacgctgag gcgcgaaagc gtggggagca 780 aacaggatta gataccctgg tagtccacgc cgtaaacgat gagtgctagg tgttaggggt 840 ttcgataccc ttggtgccga agtaaacaca ataagcactc cgcctgggga gtacgctcgc 900 aagagtgaaa ctcaaaggaa ttgacgggga cccgcacaag cagtggagta tgtggtttaa 960 ttcgaagcaa cgcgaagaac cttaccaggt cttgacatcc ctctgaccgg tacagagatg 1020 taccttccct tcggggcaga ggagacaggt ggtgcatggt tgtcgtcagc tcgtgtcgtg 1080 agatgttggg ttaagtcccg caacgagcgc aacccttgaa cttagttgcc agcattttca 1140 gttgggcact ctaagttgac tgccggtgac aaaccggagg aaggtgggga tracgtcaaa 1200 tcatcattgc cccttatgac ctgggctaca cacgtactac aatggccggt acaacgggaa 1260 gcgaagtccg cgagatggag cgaatcctta gaagccggtc tcagttcgga ttgcaggctg 1320 caactcgcct gcatgaagtc ggaattgcta gtaatcgcgg atcagcatgc cgcggtgaat 1380 acgttcccgg gtcttgtaca caccgcccgt cacaccacga gagtttacaa cacccgaagt 1440 cggtggggta accgcaagga gccagccgcc gaaggtgggg tagatgattg gggtgaagtc 1500 gtaacaaggt agccgtatcg gaagggatgc ggctggatca cctccttgcg gccgcccatt 1560 ttttttt 1567 5 1400 DNA Paenibacillus validus misc_feature (4)..(4) n=a, c, g or t 5 tctngagttt gatcntggnt caggacgaac gcnggcggag tgcctaatan atgcaagttg 60 agcggacnta tccttcganc ncaggttagc ggcggacggg tgagtaamam gtaggcaacc 120 tgcctgtaag atcgggataa ytaccggaaa cggtagctaa gaccggatag ctggtttctc 180 cgcatggggg aatcatgaaa catggggcaa cctgtggctt acggatgggc ctgcggcgca 240 ttagctagtt ggtggggtaa tggcccacca aggcgacgat gcgtagccga cctgagaggk 300 tgatcggcca acactgggac tgagacacgg cccagaytcy tacgggaggc agcagtaggg 360 aatcttccgc aatgggcgca agcctgacgg agcaacgccg cgtgagtgat gaaggttttc 420 ggatcgtaaa gctctgttgc caaggaagaa cgcctcggag agtaactgct ctgagggtga 480 cggtacttga gaagaaagcc ccggctaact acgtgccagc agccgcggta atacgtaggg 540 ggcaagcgtt gtccggaatt attgggcgta aagcgcgcgc aggcggtctt ttaagtttgg 600 tgtttaagcc cggggctcaa ccccggttcg cactgaaaac tgggagactt gagtgcagga 660 gaggaaagcg gaattccacg tgtagcggtg aaatgcgtag agatgtggag gaacaccagt 720 ggcgaaggcg gctttctgga ctgtaactga cgctgaggcg cgaaagcgtg gggagcaaac 780 aggattagat accctggtag tccacgccgt aaacgatgag tgctaggtgt taggggtttc 840 gatacccttg gtgccgaagt aaacacaata agcactccgc ctggggagta cgctcgcaag 900 agtgaaactc aaaggaattg acggggaccc gcacaagcag tggagtatgt ggtttaattc 960 gaagcaacgc gaagaacctt accaggtctt gacatccctc tgaccggtac agagatgtac 1020 cttcccttcg gggcagagga gacaggtggt gcatggttgt cgtcagctcg tgtcgtgaga 1080 tgttgggtta agtcccgcaa cgagcgcaac ccttgaactt agttgccagc antcaattgg 1140 ggnccccyaa ttkaanngcc gntaacaacc cgaagaaagg tgggaataac ttcaatcctc 1200 ctkcccccta ttaacnnggg nnnccccctt cnnnnatngg cnggtnnacc ggaaaccaaa 1260 tncccaaaat gaaccaatcc ctnaaaaccc ggccccattc cgaatngnna ggnnncacnc 1320 ccccnnctta aattcgnatt gncnattatc cccgaancac nttcccccgg naannacttc 1380 cccggttctg tttaaaaccc 1400 6 757 DNA Paenibacillus, new species misc_feature (217)..(217) n=a, c, g or t 6 ccccctggag cggcggacgg gtgagtaaca cgtaggcaac ctgcctgtaa gaccgggata 60 actaccggaa acggtagcta agaccggata ggtgattttt ccgcatggag ggatcaagaa 120 acacggtgca agctgtggct tacagatggg cytgcggcgc attagmtagt tggtggggta 180 acggctcacc aaggcgacga tgcgtagccg acctganagg gtgatcggcc acactgggac 240 tgagacacgg cccagactcc tacgggaggc agcagtaggg aatcttccgc aatggacgca 300 agtctgacgg agcaacgccg cgtgagtgaa gaaggttttc ggatcgtaaa gctctgttgc 360 caaggaagaa cgccttgggg agtcactgcc ctgagggtga cggtacttga gaagaaagcc 420 ccggctaact acgtgccagc agccgcggta atacgtaggg ggcaagcgtt gtccggaatt 480 attgggcgta aagcgcgcgc aggcggccgc ttaagtttgg tgtttaagcc cggggctcaa 540 ccccggatcg caccgaaaac tgggtggctt gagtgcagga gaggaargcg kaaaagttcc 600 acgtgtagcg gtgaaatgcg tanagatgtg gaggaacacc antggcgaaa ggcggctttc 660 tggactgtaa ctgacgctga ggcgcgaaag cgtggggagc aaacaggatt anataccctg 720 gtagtccacg ccgtaaacga tnaattgcta ngtgtta 757 7 639 DNA Paenibacillus, new species misc_feature (505)..(505) n=a, c, g or t 7 aagaaacacg gtgcaagctg tggcttacag atgggcctgc ggcgcattag ctagttggtg 60 gggtaacggc tcaccaaggc gacgatgcgt agccgacctg agagggtgat cggccacact 120 gggactgaga cacggcccag actcctacgg gaggcagcag tagggaatct tccgcaatgg 180 acgcaagtct gacggagcaa cgccgcgtga gtgaagaagg ttttcggatc gtaaagctct 240 gttgccaagg aagaacgcct tggggagtca ctgccctgag ggtgacggta cttgagaaga 300 aagccccggc taactacgtg ccagcagccg cggtaatacg tagggggcaa gcgttgtccg 360 gaattattgg gcgtaaagcg cgcgcaggcg gccgcttaag tttggtgtat aagcccgggg 420 ctcaaccccg gatcgcaccg aaaactgggt ggcttgagtg caggagagga aagcggaatt 480 ccacgtgtag cggtgaaatg cgtanagatg tggaggaaca ccantggcga aggcggcttt 540 ctggactgta actgacgctg aggcgcgaaa gcgtggggag caaacaggat tanataccct 600 ggtantccac gccgtaaacg atgaatgcta ngtgttagg 639 8 1551 DNA Paenibacillus, new species 8 cctagagttt gatcctggct caggacgaac cgctggcggc gtgcctaata catgcaagtc 60 gagcgctagg ggtgctccct taggggagac ctcctggagc ggcggacggg tgagtaacac 120 gtaggcaacc tgcctgtaag accgggataa ctaccggaaa cggtagctaa gaccggatag 180 gtggtttctc cgcatggagg gatcaagaaa cacggtgcaa gctgtggctt acagatgggc 240 ctgcggcgca ttagctagtt ggtggggtaa cggctcacca aggcgacgat gcgtagccga 300 cctgagaggg tgatcggcca cactgggact gagacacggc ccagactcct acgggaggca 360 gcagtaggga atcttccgca atggacgcaa gtctgacgga gcaacgccgc gtgagtgaag 420 aaggttttcg gatcgtaaag ctctgttgcc aaggaagaac gccttgggga gtcactgccc 480 tgagggtgac ggtacttgag aagaaagccc cggctaacta cgtgccagca gccgcggtaa 540 tacgtagggg gcaagcgttg tccggaatta ttgggcgtaa agcgcgcgca ggcggccgct 600 taagtttggt gtataagccc ggggctcaac cccggatcgc accgaaaact gggtggcttg 660 agtgcaggag aggaaagcgg aattccacgt gtagcggtga aatgcgtaga gatgtggagg 720 aacaccagtg gcgaaggcgg ctttctggac tgtaactgac gctgaggcgc gaaagcgtgg 780 ggagcaaaca ggattagata ccctggtagt ccacgccgta aacgatgagt gctaggtgtt 840 aggggtttcg atacccttgg tgccgaagtc aacacaataa gcactccgcc tggggagtac 900 gctcgcaaga gtgaaactca aaggaattga cggggacccg cacaagcagt ggagtatgtg 960 gtttaattcg aagcaacgcg aagaacctta ccaggtcttg acatcccttt gaccggtaca 1020 gagatgtacc tttccttcgg gacagaggag acaggtggtg catggttgtc gtcagctcgt 1080 gtcgtgagat gttgggttaa gtcccgcaac gagcgcaacc cttgagctta gttgccagca 1140 ttaagttggg cactctaagt tgactgccgg tgacaaaccg gaggaaggtg gggatgacgt 1200 caaatcatca tgccccttat gacctgggct acacacgtac tacaatggcc ggtacaacgg 1260 gaagcgaagg agcgatccgg agcgaatcct tataagccgg tctcagttcg gattgcaggc 1320 tgcaactcgc ctgcatgaag tcggaattgc tagtaatcgc ggatcagcat gccgcggtga 1380 atacgttccc gggtcttgta cacaccgccc gtcacaccac gagagtttac aacacccgaa 1440 gtcggtgggg taaccgcaag gagccagccg ccgaaggtgg ggtagatgat tggggtgaag 1500 tcgtaagcaa ggtagccgta tcggaaggtg cggctggatc acctccttaa a 1551 9 1476 DNA Paenibacillus, new species misc_feature (256)..(256) n=a, c, g or t 9 tcccttaggg gagacctcct ggagcggcgg acgggtgagt aacacgtagg caacctgcct 60 gtaagaccgg gataactacc ggaaacggta gctaagaccg gataggtgat ttctccgcat 120 ggagggatca agaaacacgg tgcaagctgt ggyttacaga tgggcctgcg gcgcattagc 180 tagttggtgg ggtaacggct maccaagttg cgacgatgcg tagccgacct gagagggtga 240 tcggccacac tgggantgag acacggccca gactcntacg ggaggcagca gtagggaatc 300 ttccgcaatg gacgcaagtc tgacggagca acgccgcgtg agtgaagaag gttttcggat 360 cgtaaagctc tgttgccaag gaagaacgcc ttggggagtc actgccctga gggtgacggt 420 acttgagaag aaagccccgg ctaactacgt gccagcagcc gcggtaatac gtagggggca 480 agcgttgtcc ggaattattg ggcgtaaagc gcgcgcaggc ggccgcttaa gtttggtgta 540 taagcccggg gctcaacccc ggatcgcacc gaaaactggg tggcttgagt gcaggagagg 600 aaagcggaat tccacgtgta kcggtgaaat gcgtagagat gtggaggaac accagtggcg 660 aaggcggctt tctggactgt aactgacgct gaggcgcgaa agcgtgggga gcaaacagga 720 ttagataccc tggtagtcca cgccgtaaac gatgagtgct aggtgttagg ggtttcgata 780 cccttggtgc cgaagtcaac acaataagca ctccgcctgg ggagtacgct cgcaagagtg 840 aaacttaaag gaattgacgg ggacccgcac aagcagtgga gtatgtggtt taattcgaag 900 caacgcgaag aaccttacca ggtcttgaca tccctttgac cggtacagag atgtaccttt 960 ccttcgggac agaggagaca ggtggtgcat ggttgtcgtc agctcgtgtc gtgagatgtt 1020 gggttaagtc ccgcaacgag cgcaaccctt gagcttagtt gccagcatta agttgggcac 1080 tctaagttga ctgccggtga caaaccggag gaaggtgggg atgacgtcaa atcatcatgc 1140 cccttatgac ctgggctaca cacgtactac aatggccggt acaacgggaa gcgaaggagc 1200 gatccggagc gaatccttat aagccggtct cagttcggat tgcaggctgc aactcgcctg 1260 catgaagtcg gaattgctag taatcgcgga tcagcatgcc gcggtgaata cgttcccggg 1320 tcttgtacac accgcccgtc acaccacgag agtttacaac acccgaagtc ggtggggtaa 1380 ccgcaaggag ccagccgccg aaggtggggt agatgattgg ggtgaagtcg taacaaggta 1440 gccgtatcgg aaggtgcggc tggatcacct ccttaa 1476 10 1545 DNA Paenibacillus, new species misc_feature (2)..(2) n=a, c, g or t 10 tngngtttga tnctgggtta ggacggaagn tggnggggtg cctaatacat gcaagtcgag 60 cgctaggggt gctcccttag gggagccccc ctggagcggc ggacgggtga gtaacacgta 120 ggcaacctgc ctgtaagacc gggataacta ccggaaacgg tagctaagac cggataggtg 180 atttttccgc atggagggat caagaaacac ggtgcaagct gtggcttaca gatgggcctg 240 cggcgcatta gctagttggt ggggtaacgg ctcaccaagg cgacgatgcg tagccgacct 300 gagaggtgat cggccacact gggatgagac acggcccaga ctctacggga ggcagcagta 360 gggaatcttc cgcaatggac gcaagtctga cggagcaacg ccgcgtgagt gaagaaggtt 420 ttcggatcgt aaagctctgt tgccaaggaa gaacgccttg gggagtcact gccctgaggg 480 tgacggtact tgagaagaaa gccccggcta actacgtgcc agcagccgcg gtaatacgta 540 gggggcaagc gttgtccgga attattgggc gtaaagcgcg cgcaggcggc cgcttaagtt 600 tggtgtataa gcccggggct caaccccgga tcgcaccgaa aactgggtgg cttgagtgca 660 ggagaggaaa gcgggaattc cacgtgtagc ggtgaaatgc gtagagatgt ggaggaacac 720 cagtggcgaa ggcggctttc tggactgtaa ctgacgctga ggcgcgaaag cgtggggagc 780 aaacaggatt agataccctg gtagtccacg ccgtaaacga tgagtgctag gtgttagggg 840 tttcgatacc cttggtgccg aagtcaacac aataagcact ccgcctgggg agtacgctcg 900 caagagtgaa actcaaagga attgacgggg acccgcacaa gcagtggagt atgtggttta 960 attcgaagca acgcgaagaa ccttaccagg tcttgacatc cctctgaccg gtacagagat 1020 gtacctttcc ttcgggacag aggagacagg tggtgcatgg ttgtcgtcag ctcgtgtcgt 1080 gagatgttgg gttaagtccc gcaacgagcg caacccttga gcttagttgc cagcattaag 1140 ttgggcactc taagttgact gccggtgaca aaccggagga aggtggggat gacgtcaaat 1200 catcatgccc cttatgacct gggctacaca cgtactacaa tggccggtac aacgggaagc 1260 gaaggagcga tccggagcaa atccttataa gccggtctca gttcggattg caggctgcaa 1320 ctcgcctgca tgaagtcgga attgctagta atcgcggatc agcatgccgc ggtgaatacg 1380 ttcccgggtc ttgtacacac cgcccgtcac accacgagag tttacaacac ccgaagtcgg 1440 tggggtaacc gcaaggagcc agccgccgaa ggtggggtag atgattgggg tgaagtcgta 1500 acaaggtagc cgtatcggaa ggtgcggctg gatcacctcc ttaaa 1545 11 1554 DNA Paenibacillus, new species misc_feature (3)..(3) n=a, c, g or t 11 ttnagngttt gatcctggnt naggnngnaa ggtggnggng tgcctaanaa angcaagttg 60 ngnggtaggg gtgntccctt aggggagncc ccctggagcg gcggacgggt gagtaacacg 120 gtaggcaacy tgcctgtaag accgggataa ctaccggaaa cggtagctaa gaccggatag 180 gtgatttttc cgcatggagg gatcaagaaa cacggtgcaa gctgtggctt acagatgggc 240 ctgyggcgca twagytagtt ggtggggtaa cggctcacca aggcgacgat gcgtagccga 300 cctgagaggg tgatcggcca cactgggact gagacacggc ccagactcct acgggaggca 360 gcagtagngg aatcttccsc aatggacgca agtctgacgg agcaacgccg cgtgagtgaa 420 gaaggttttc ggatcgtaaa gctctgttgc caaggaagaa cgccttgggg agtcactgcc 480 ctgagggtga cggtacttga gaagaaagcc ccggctaayt acgtgccagc agccgcggta 540 atacgtaggg ggcaagcgtt gtccggaatt attgggcgta aagcgcgcgc aggcggccgc 600 ttaagtttgg tgtttaagcc cggggctcaa ccccggatcg caccgaaaac tgggtggctt 660 gagtgcagga gaggaaagcg gaattccacg tgtagcggtg aaatgcgtag agatgtggag 720 gaacaccagt ggcgaaggcg gctttctgga ctgtaactga cgctgaggcg cgaaagcgtg 780 gggagcaaac aggattagat accctggtag tccacgccgt aaacgatgag tgctaggtgt 840 taggggtttc gatacccttg gtgccgaagt caacacaata agcactccgc ctgtgrragt 900 acgntngcaa gagtgaaact caaaggaatt gacggggacc cgcacaagca gtggagtatg 960 tggtttaatt cgaagcaacg cgaagaacct taccaggtct tgacatccct ctgaccggta 1020 cagagatgta cctttccttc gggacagagg agacaggtgg tgcatggttg tcgtcagctc 1080 gtgtcgtgag atgttgggtt aagtcccgca acgagcgcaa cccttgagct tagttgccag 1140 cattaagttg ggcactctaa gttgactgcc ggtgacaaac cggaggaagg tggggatgac 1200 gtcaaatcat catgcccctt atgacytggg ctacacacgt actacaatgg ccggtacaac 1260 gggaagcgaa ggagcgatcc ggagcgaatc cttataagcc ggtctcagtt cggattgcag 1320 gctgcaactc gcctgcatga agtcggaatt gctagtaatc gcggatcagc atgccgcggt 1380 gaatacgttc ccgggtcttg tacacaccgc ccgtcacacc acgagagttt acaacacccg 1440 aagtcggtgg ggtaaccgca aggagccagc cgccgaaggt ggggtagatg attggggtga 1500 agtcgtaaca aggtcagccg tatcggaagg tgcggctgga tcacctcctt aaaa 1554 

What is claimed:
 1. An isolated bacterial strain for bioremediation, that is in the family Bacillaceae, and degrades at least two polyaromatic hydrocarbons selected from the group consisting of naphthalene, phenanthrene and biphenyl.
 2. The isolated bacterial strain of claim 1, that is induced by phenanthrene to degrade pyrene.
 3. The isolated bacterial strain of claim 1 that is in the genus Paenibacillus.
 4. The isolated bacterial strain of claim 3 that is in the species Paenibacillus validus.
 5. The isolated bacterial strain of claim 4, that is selected from the group consisting of isolates PR-P1, PR-N4 and PR-B2.
 6. The isolated bacterial strain of claim 5, that is selected from the group consisting of ATCC Accession No. [not yet assigned], ATCC Accession No. [not yet assigned] and ATCC Accession No. [not yet assigned].
 7. An isolated bacterial strain for bioremediation that is Paenibacillus napthalenovorans and degrades naphthalene.
 8. The isolated bacterial strain of claim 7, which has a whole cell fatty acid composition when grown on trypticase soy agar at 28° C. for 24 hours in which 16:1 ω11c fatty acids comprise at least 8.8%.
 9. The isolated bacterial strain of claim 8, in which the whole cell fatty acid composition when grown on trypticase soy agar at 28° C. for 24 hours further comprises at least 5.8% but not more than 10.0% 17:0 anteiso fatty acids.
 10. The isolated bacterial strain of claim 7, having a whole cell fatty acid similarity index, as compared to isolate PR-N1, of greater than 0.4 when both are grown on trypticase soy agar at 28° C. for 24 hours.
 11. The isolated bacterial strain of claim 7, having a 16S rRNA gene sequence that is at least about 95% homologous to SEQ ID NO:8.
 12. The isolated bacterial strain of claim 7, having a genomic DNA of which at least 15% binds to genomic DNA of isolate PR-N1.
 13. The isolated bacterial strain of claim 7, which is ATCC Accession No. [not yet assigned].
 14. A plurality of isolated bacterial strains for bioremediation comprising at least two strains selected from the group consisting of Paenibacillus validus, a sphingomonad, an Arthrobacter, Paenibacillus napthalenovorans and a nocardioform.
 15. The plurality of bacterial strains of claim 14, in which the P. napthalenovorans strain is ATCC Accession No. [not yet assigned], and the P. validus strain is selected from the group consisting of ATCC Accession No. [not yet assigned], ATCC Accession No. [not yet assigned] and ATCC Accession No. [not yet assigned].
 16. A composition for bioremediation, comprising the bacteria of claim 1 and a ecologically acceptable carrier.
 17. A composition for bioremediation, comprising the bacteria of claim 6 and a ecologically acceptable carrier.
 18. A composition for bioremediation, comprising the bacteria of claim 13 and a ecologically acceptable carrier.
 19. A method for removing polyaromatic hydrocarbons from a substrate, comprising contacting the substrate with the at least one isolated bacterial strain selected from the group consisting of the isolated bacterial strain of claim 1 and the isolated bacterial strain of claim 6, for a time sufficient to effect removal of the polyaromatic hydrocarbon.
 20. The method of claim 19, wherein the substrate is solid.
 21. The method of claim 19, wherein the substrate is liquid.
 22. The method of claim 21, wherein the substrate is aerated.
 23. The method of claim 19, which additionally comprises the step of planting plants in the substrate.
 24. The method of claim 23, wherein the plant is Spartina alterniflora.
 25. The method of claim 19, which additionally has the step of inducing the bacteria with phenanthrene.
 26. A method to isolate endospore-forming PAH-degrading bacterial strains from a heterogenous culture comprising the steps of growing the bacterial culture with a PAH as the sole carbon source and heating the culture to a temperature and for a time sufficient to kill vegetative bacteria.
 27. The method of claim 26, in which the PAH is selected from a group consisting of naphthalene, phenanthrene and bi-phenyl.
 28. The method of claim 26, in which the heat treatment step comprises heating to 70 to 90° C. for 10 to 20 minutes. 